WO2019153217A1 - Method for recovering high-performance carbon fiber from inorganic cementing material - Google Patents

Method for recovering high-performance carbon fiber from inorganic cementing material Download PDF

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WO2019153217A1
WO2019153217A1 PCT/CN2018/075922 CN2018075922W WO2019153217A1 WO 2019153217 A1 WO2019153217 A1 WO 2019153217A1 CN 2018075922 W CN2018075922 W CN 2018075922W WO 2019153217 A1 WO2019153217 A1 WO 2019153217A1
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carbon fiber
acid
recovered
sample
catalyst
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PCT/CN2018/075922
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French (fr)
Chinese (zh)
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朱继华
苏玫妮
陈丕钰
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深圳大学
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Priority to CN201880000082.6A priority Critical patent/CN109153051A/en
Priority to PCT/CN2018/075922 priority patent/WO2019153217A1/en
Publication of WO2019153217A1 publication Critical patent/WO2019153217A1/en

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    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B3/00Destroying solid waste or transforming solid waste into something useful or harmless
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B09DISPOSAL OF SOLID WASTE; RECLAMATION OF CONTAMINATED SOIL
    • B09BDISPOSAL OF SOLID WASTE NOT OTHERWISE PROVIDED FOR
    • B09B5/00Operations not covered by a single other subclass or by a single other group in this subclass

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  • the present invention relates to the recovery and reuse of carbon fibers, and more particularly to a method for recovering high performance carbon fibers from inorganic cementitious materials.
  • Carbon fiber has the advantages of high tensile strength, high Young's modulus, strong corrosion resistance, inert atmosphere resistance to ultra high temperature, excellent electromagnetic wave shielding, good biocompatibility and soft plasticity.
  • carbon fiber preparation technology has developed a wide variety of carbon fiber materials such as viscose carbon fiber, polyacrylonitrile fiber (PAN), asphalt fiber, polybenzimidazole fiber and polyester fiber.
  • CFRP Carbon Fiber Reinforced Plastic
  • CFRP can be cured by organic epoxy resin cementing material, pasted or placed on the surface or inside of the structure to improve the structural bearing capacity.
  • the epoxy resin gel contains a plurality of polar groups and an active epoxy group, and the epoxy cured product has a large cohesive strength, so the bonding strength is high.
  • due to the aging resistance, corrosion resistance and heat and humidity resistance of epoxy resin, anti-stripping, anti-cracking and impact resistance are not high.
  • inorganic cementing materials have also been used in civil engineering, such as Cement-based materials such as modified cement paste, mortar and/or concrete, or base hair materials, etc., are bonded to CFRP to form a carbon fiber-reinforced inorganic (cement-based) composite material, thereby reinforcing the building structure.
  • the inorganic cementitious material has excellent mechanical properties such as excellent corrosion resistance, high strength and toughness, and is well bonded to traditional civil engineering structural materials such as cement or concrete. Therefore, the reinforcing material (CFRP) and the original structure can work together and the reinforcing performance. better.
  • the present invention provides a method for recovering high-performance carbon fiber from inorganic cementitious materials which is technically feasible, simple in operation, high in economic efficiency and environmental protection, and is not only beneficial for recycling and reuse of carbon fiber materials, but also can solve construction.
  • the problem of garbage disposal has important economic and social significance.
  • the main object of the present invention is to provide a method for recovering high-performance carbon fiber from an inorganic cementing material, wherein the carbon fiber recycling method provided by the invention has the advantages of simple process steps, low difficulty, high recovery rate, low cost and low fiber damage. Etc.
  • Another object of the present invention is to provide a method for recovering high-performance carbon fibers from an inorganic cementing material, wherein the carbon fiber recovery method provided by the present invention can not only recover carbon fibers, but also simultaneously recover resin materials and decompose inorganic gelation.
  • Another object of the present invention is to provide a method for recovering high-performance carbon fibers from an inorganic cementing material, wherein the carbon fiber recovery method provided by the present invention has low toxicity, low requirements on production equipment, and reaction conditions. mild.
  • the carbon fiber recovery method provided by the present invention does not require shearing and/or crushing treatment of the carbon fiber reinforced composite material, and therefore, materials of any size can be recovered. At the same time, it is not necessary to shear and/or crush the carbon fiber reinforced composite material, and the mechanical properties of the recovered carbon fiber material are hardly damaged, and the economic value of the recovered carbon fiber material is higher.
  • Another object of the present invention is to provide a composition for recovering high performance carbon fibers from an inorganic cementitious material.
  • a method for recovering high performance carbon fibers from an inorganic cementitious material capable of achieving the foregoing and other objects and advantages includes the following steps:
  • step (C) further comprises the step of:
  • step (D) wherein the carbon fiber recyclate surface is provided with spaced apart pores according to step (D).
  • step (D) wherein according to step (D), the interval between each of the holes is greater than 0.1 mm, the flushing water pressure is higher than 0.1 MPa, and the rinsing time is not less than 3 seconds.
  • the present invention further provides an electrolyte for recovering high performance carbon fibers from an inorganic cementitious material, comprising:
  • Figure 1A shows a schematic structural view of a carbon fiber electrochemical recovery system.
  • FIGS. 1B and 1C are schematic views showing the structure of a carbon fiber reinforced cement-based composite test piece.
  • Figure 2 shows a carbon fiber recyclate recovered from a carbon fiber reinforced cementitious composite.
  • Figure 3A shows the interface between the cementitious and carbon fibers of a carbon fiber reinforced cementitious material that has not been electrochemically recycled.
  • Figure 3B shows a detail enlargement of the portion of the block in Figure 3A.
  • Figure 3C shows the interface between the cementitious material of the carbon fiber recyclate and the carbon fiber.
  • Figure 3D shows a detail enlargement of the portion of the block in Figure 3C.
  • Figure 4 shows the amount of carbon fiber recovered from samples of different grouped carbon fiber reinforced cementitious composites.
  • Figure 5 shows the voltages of different groups of carbon fiber reinforced cementitious composite samples during the reaction.
  • Figure 6 shows the tensile strength of carbon fiber monofilaments recovered from different groups of carbon fiber reinforced cementitious composite samples.
  • Figure 7 shows the interfacial shear strength of recycled carbon fibers from different grouped carbon fiber reinforced cementitious composite samples.
  • Figure 8A shows the surface failure mode of the carbon fiber precursor.
  • Figure 8B shows the surface failure mode of the carbon fiber recovered from the I20S 2.0 H 1 carbon fiber reinforced cementitious composite sample.
  • Figure 8C shows the surface failure mode of the carbon fiber recovered from the I40S 2.0 H 1 carbon fiber reinforced cementitious composite sample.
  • Figure 8D shows the surface failure mode of the carbon fiber recovered from the I20S 2.0 H 3 carbon fiber reinforced cementitious composite sample.
  • Figure 8E shows the surface failure mode of the carbon fiber recovered from the I40S 2.0 H 3 carbon fiber reinforced cementitious composite sample.
  • Figure 8F shows the surface failure mode of the carbon fiber recovered from the I20S 2.0 H 5 carbon fiber reinforced cementitious composite sample.
  • Figure 8G shows the surface failure mode of the carbon fiber recovered from the I40S 2.0 H 5 carbon fiber reinforced cementitious composite sample.
  • Figure 9A shows an SEM scan image of the surface of a carbon fiber precursor.
  • Figure 9B shows an SEM scan of the carbon fiber recovered from the I20S 2.0 H 1 carbon fiber reinforced cementitious composite sample.
  • Figure 9C shows an SEM scan of carbon fiber recovered from a sample of I40S 2.0 H 1 carbon fiber reinforced cementitious composite.
  • Figure 9D shows an SEM scan of the carbon fiber recovered from the I20S 2.0 H 3 carbon fiber reinforced cementitious composite sample.
  • Figure 9E shows a SEM scan of the carbon fiber recovered from the I40S 2.0 H 3 carbon fiber reinforced cementitious composite sample.
  • Figure 9F shows an SEM scan of the carbon fiber recovered from the I20S 2.0 H 5 carbon fiber reinforced cementitious composite sample.
  • Figure 9G shows an SEM scan of the carbon fiber recovered from the I40S 2.0 H 5 carbon fiber reinforced cementitious composite sample.
  • Figures 10A and 10B show AFM scan images of the surface of a carbon fiber precursor.
  • Figures 10C and 10D show AFM scan images of recovered carbon fibers from a sample of I20S 2.0 H 1 carbon fiber reinforced cementitious composites.
  • 10E and 10F show AFM scan images of recovered carbon fibers of a sample of I40S 2.0 H 1 carbon fiber reinforced cementitious composite.
  • Figures 10G and 10H show AFM scan images of recycled carbon fibers from a sample of I20S 2.0 H 3 carbon fiber reinforced cementitious composites.
  • 10I and 10J show a table AFM scan image of the recovered carbon fiber of the I40S 2.0 H 3 carbon fiber reinforced cementitious composite sample.
  • Figures 10K and 10L show AFM scan images of carbon fibers recovered from samples of the I20S 2.0 H 5 carbon fiber reinforced cementitious composite.
  • Figure 10M and Figure 10N show AFM scan images of recycled carbon fibers from a sample of I40S 2.0 H 5 carbon fiber reinforced cementitious composites.
  • Figure 11A shows an XPS (X-ray photoelectron spectroscopy) full spectrum image of the surface of a carbon fiber precursor.
  • Figure 11B shows an XPS scan C1s high resolution narrow spectrum image of the surface of a carbon fiber precursor.
  • Figure 11C shows an XPS-scan full-spectrum image of carbon fiber recovered from a sample of I20S 2.0 H 1 carbon fiber reinforced cementitious composite.
  • Figure 11D shows an XPS scan C1s high resolution narrow-spectrum image of carbon fiber recovered from a sample of I20S 2.0 H 1 carbon fiber reinforced cementitious composite.
  • Figure 11E shows an XPS-scan full-spectrum image of carbon fiber recovered from a sample of I20S 2.0 H 3 carbon fiber reinforced cementitious composites.
  • Figure 11F shows a high resolution narrow-spectrum image of XPS scan C1s of carbon fiber recovered from a sample of I20S 2.0 H 3 carbon fiber reinforced cementitious composite.
  • Figure 11G shows an XPS-scan full-spectrum image of the carbon fiber recovered from the I20S 2.0 H 5 carbon fiber reinforced cementitious composite sample.
  • Figure 11H shows a high-resolution narrow-spectrum image of XPS scan C1s of carbon fiber recovered from I20S 2.0 H 5 carbon fiber reinforced cementitious composite samples.
  • Figure 12 shows the amount of carbon fiber recovered from carbon fiber reinforced cementitious composite samples at different temperatures.
  • Figure 13 shows the voltage of a carbon fiber reinforced cementitious composite sample during the reaction at different temperatures.
  • Figure 14 shows the tensile strength of monofilaments of carbon fibers recovered from carbon fiber reinforced cementitious composite samples at different temperatures.
  • Figure 15 shows the interfacial shear strength of carbon fibers recovered from carbon fiber reinforced cementitious composite samples at different temperatures.
  • Figure 16A shows the surface failure mode of carbon fiber recovered from a sample of I20S 2.0 H 3 T 1 carbon fiber reinforced cementitious composite.
  • Figure 16B shows the surface failure mode of the carbon fiber recovered from the I40S 2.0 H 1 carbon fiber reinforced cementitious composite sample.
  • Figure 16C shows the surface failure mode of the carbon fiber recovered from the I20S 2.0 H 3 T 2 carbon fiber reinforced cementitious composite sample.
  • Figure 16D shows the surface failure mode of the carbon fiber recovered from the I40S 2.0 H 3 T 2 carbon fiber reinforced cementitious composite sample.
  • Figure 16E shows the surface failure mode of the carbon fiber recovered from the I20S 2.0 H 3 T 3 carbon fiber reinforced cementitious composite sample.
  • Figure 16F shows the surface failure mode of the carbon fiber recovered from the I40S 2.0 H 3 T 3 carbon fiber reinforced cementitious composite sample.
  • Figure 17A shows an SEM scan of the carbon fiber recovered from the I20S 2.0 H 3 T 1 carbon fiber reinforced cementitious composite sample.
  • Figure 17B shows an SEM scan of the carbon fiber recovered from the I40S 2.0 H 3 T 1 carbon fiber reinforced cementitious composite sample.
  • Figure 17C shows an SEM scan of the carbon fiber recovered from the I20S 2.0 H 3 T 2 carbon fiber reinforced cementitious composite sample.
  • Figure 17D shows an SEM scan of the carbon fiber recovered from the I40S 2.0 H 3 T 2 carbon fiber reinforced cementitious composite sample.
  • Figure 17E shows a SEM scan of the carbon fiber recovered from the I20S 2.0 H 3 T 3 carbon fiber reinforced cementitious composite sample.
  • Figure 17F shows an SEM scan of the carbon fiber recovered from the I40S 2.0 H 3 T 3 carbon fiber reinforced cementitious composite sample.
  • Figure 18A shows an XRD scan of carbon fibers recovered from I20S 2.0 carbon fiber reinforced cementitious composite samples at different temperature gradients.
  • Figure 18B shows an XRD scan of carbon fibers recovered from I40S 2.0 carbon fiber reinforced cementitious composite samples at different temperature gradients.
  • Figure 19A shows an XPS-scan full-spectrum image of carbon fiber recovered from a sample of the I20S 2.0 H 3 T 1 carbon fiber reinforced cementitious composite.
  • Figure 19B shows a high resolution narrow-spectrum image of XPS scan C1s of carbon fiber recovered from a sample of I20S 2.0 H 3 T 1 carbon fiber reinforced cementitious composite.
  • Figure 19C shows an XPS-scan full-spectrum image of the carbon fiber recovered from the I20S 2.0 H 3 T 2 carbon fiber reinforced cementitious composite sample.
  • Figure 19D shows an XPS scan C1s high resolution narrow-spectrum image of carbon fiber recovered from a sample of I20S 2.0 H 3 T 2 carbon fiber reinforced cementitious composite.
  • Figure 19E shows an XPS-scan full-spectrum image of the carbon fiber recovered from the I20S 2.0 H 3 T 3 carbon fiber reinforced cementitious composite sample.
  • Figure 19F shows an XPS scan C1s high resolution narrow-spectrum image of carbon fiber recovered from a sample of I20S 2.0 H 3 T 3 carbon fiber reinforced cementitious composite.
  • Figure 20A shows an XRD scan of carbon fibers recovered from I20S 2.0 carbon fiber reinforced cementitious composite samples at various catalyst concentrations.
  • Figure 20B shows an XRD scan of carbon fibers recovered from I40S 2.0 carbon fiber reinforced cementitious composite samples at various catalyst concentrations.
  • a method for recovering high performance carbon fibers from an inorganic cementitious material in accordance with a preferred embodiment of the present invention is described in detail, and an exemplary embodiment is explained using a carbon fiber reinforced cementitious material.
  • the method wherein the method for recovering carbon fibers from a carbon fiber reinforced cement-based composite material (waste) comprises the steps of:
  • the method for recovering high-performance carbon fibers from the inorganic cementing material is in the step (C). Then further steps are included:
  • electrolyte refers to the inclusion of NaCl, water, and a catalyst that is used to recover carbon fibers from a carbon fiber reinforced cementitious composite.
  • the NaCl concentration is measured in weight percent, for example, the NaCl concentration may be x1 (0.5%), x2 (1%), x3 (2%), and x4 (3%).
  • the current (I) size is measured in mA, such as 20 mA, 40 mA.
  • the grouping and experimental parameters of specific carbon fiber reinforced cement-based composites are shown in Table 5.1.
  • the number of carbon fiber reinforced cement-based composite specimens is determined by the applied current intensity, NaCl concentration, HNO 3 concentration and temperature, such as the test piece number “I20S”.
  • the first part “I20” means that the constant current intensity applied by the test piece is 20 mA
  • the second part “S 2.0 ” means that the concentration of NaCl in the electrolyte is 2% of the mass of deionized water
  • the third part “H 3” means that the concentration of HNO 3 added per liter of the electrolyte is 3 g/L.
  • the fourth part “T 40” means that the temperature of the electrolyte is maintained at 40 ° C during the experiment. Without the fourth part, the test is carried out at room temperature (temperature is 25 degrees)
  • the (electrochemical) recovery system for recovering carbon fibers from CFRP reinforced cement-based composite materials includes a DC power source to provide a unidirectional operating current for the system; a cathode-anode material in which the carbon fiber reinforced cement base to be recovered
  • the composite plate (recycled sample) is connected as an anode to the positive electrode of the power supply, the stainless steel piece is connected as a cathode to the negative electrode of the power source;
  • the electrolyte contains NaCl, water (solvent) and a catalyst;
  • the data log (Datalog) is connected in parallel with the recovered sample and the stainless steel piece. , monitor sample voltage changes.
  • the carbon fiber reinforced cementitious composite panel is placed in parallel with the stainless steel sheet and the distance between the two is fixed at 50 mm.
  • the carbon fiber recovered material recovered from the carbon fiber reinforced cement-based composite material is soft in texture by point chemical treatment.
  • the interface between the cement-based and carbon fibers of the carbon fiber reinforced cement-based material which is not electrochemically treated has a rib-shaped groove structure which is complete and regular and can form a strong bond with carbon fibers.
  • the mechanical bite is used, the interface has only very small holes, and no cracks and other defects are visible.
  • the regular rhombic groove structure of the interface between the cement-based material of the carbon fiber recyclate and the carbon fiber interface has been divided into broken small units by large cracks in the longitudinal and lateral directions. Fluffy, and there are many large crack holes in which the porosity increases sharply, the interface has completely lost the mechanical bite with carbon fiber, and the adhesion is greatly reduced.
  • the amount of carbon fiber recovered from different carbon fiber reinforced cement-based composite samples is different.
  • the carbon fiber recovery increases first and then decreases with the increase of HNO 3 concentration, and the concentration of HNO 3 is 3g.
  • the concentration of HNO 3 is 3g.
  • the amount of carbon fiber recovered is the largest.
  • the amount of carbon fiber recovered was significantly reduced.
  • the voltage variation of different groups of carbon fiber reinforced cementitious composite samples during the reaction As shown in Figure 5 of the accompanying drawings, the voltage variation of different groups of carbon fiber reinforced cementitious composite samples during the reaction.
  • the H 0 group has the highest voltage and the highest relative fluctuation;
  • the H 5 group has lower voltage than the H 0 group, but it is still relatively high;
  • the H 3 and H 1 groups have lower sample voltages.
  • the I40 series sample voltage is larger than the I20 series
  • the S 3.0 series sample voltage is larger than the S 2.0 series.
  • the surface failure mode of the carbon fiber precursor is DB.
  • the surface damage mode of the carbon fiber recovered from the I20S 2.0 H 1 carbon fiber reinforced cement-based composite sample is DB.
  • the surface failure mode of the carbon fiber recovered from the I40S 2.0 H 1 carbon fiber reinforced cementitious composite sample is DB.
  • the surface failure mode of the carbon fiber recovered from the I20S 2.0 H 3 carbon fiber reinforced cement-based composite sample is CB.
  • the surface failure mode of the carbon fiber recovered from the I40S 2.0 H 3 carbon fiber reinforced cement-based composite sample is CB.
  • the surface damage mode of the carbon fiber recovered from the I20S 2.0 H 5 carbon fiber reinforced cementitious composite sample is CB.
  • the surface failure mode of the carbon fiber recovered from the I40S 2.0 H 5 carbon fiber reinforced cement-based composite sample is EB.
  • the SEM scan image of the surface of the carbon fiber precursor shows that the surface is smooth.
  • the carbon fiber surface of the I20S 2.0 H 3 group and the I40S 2.0 H 3 carbon fiber reinforced cement matrix composite sample is clean, and few cement gel particles remain, but A cross-crack is found on the surface of the carbon fiber of individual numbers, and a weak layer is formed at the crack, resulting in a decrease in the tensile strength of the carbon fiber.
  • the carbon fiber surface of the I20S 2.0 H 5 group and the I40S 2.0 H 5 carbon fiber reinforced cement matrix composite sample is recovered, and many cement gel particles are found on the surface of the carbon fiber. Longitudinal cracks and transverse cracks, and the depth is not shallow, reducing the force cross section of the carbon fiber, so the tensile strength of the carbon fiber recovered by the H 5 series is seriously degraded.
  • the AFM scan image of the carbon fiber recovered from each of the grouped carbon fiber reinforced cementitious composite samples shows that when the concentration of HNO 3 is low, a small amount of oxidation of the electrochemical recovery process is shown.
  • the etch will increase the interfacial shear strength of the carbon fiber, and when the HNO 3 concentration is increased to a certain extent, the excessive oxidative etching reduces the interfacial shear strength of the carbon fiber.
  • the amount of carbon fiber recovered from the carbon fiber reinforced cement-based composite sample at different temperatures shows a high first and then a low temperature, and the carbon fiber is recovered at a temperature of 40 ° C. The largest amount.
  • the voltage of the carbon fiber reinforced cement-based composite sample during the reaction process at different temperature conditions indicates that the voltage of the carbon fiber reinforced cement-based composite sample is low, and the voltage difference values of different grouped samples are very high. Small, indicating that under high temperature conditions, the system resistance of the sample is very small, and the voltage of all samples is basically stable during the electrochemical recovery cycle.
  • the surface failure mode of the carbon fiber recovered from the sample of each group of carbon fiber reinforced cement-based composite materials except that the failure mode of I40S 2.0 H 3 T 2 is CB, the failure mode of other samples Both are DB.
  • the defects of the surface cracks of the carbon fiber obtained by the recovery of the sample of the carbon fiber reinforced cement-based composite materials are less, indicating that the recovery cycle is shortened to reduce the oxidation and corrosion of the recovery process.
  • the carbon fiber reinforced cement-based composite material of this experiment consists of two major parts, CFRP and cement-based cementitious materials.
  • the CFRP material is selected from the HITEX-C300 carbon fiber cloth produced by Nanjing Haituo Composite Materials Co., Ltd., which is a 12K unidirectional woven fabric with a density of 300g/m2.
  • the cement is selected from the China Resources brand PO42.5R ordinary composite Portland cement produced in Dongguan.
  • the silicon powder is a Siken silicon powder produced in Shanghai, and the high molecular polymer is a redispersible powder of the DY-5025 (Germany) model.
  • the carbon fiber short yarn produced by Hong Kong Kaben Co., Ltd. is selected to have a length of about 3 mm.
  • Sodium chloride (analytical grade) and HNO 3 (analytical grade) produced by Xiqiao Chemical Co., Ltd. were selected. The mass fraction of sodium chloride was 99.5%, and the mass fraction of B was 65%-68%.
  • the carbon fiber cloth is in the middle, and the specific composition and content of the cement-based material are shown in Table 1.1.
  • the carbon fiber reinforced cement-based composite test piece has a size of 30 mm ⁇ 245 mm ⁇ 4 mm.
  • the cement material is about 2 mm thick on the upper and lower sides, and the carbon fiber cloth is in the middle, as shown in FIG. 1B and FIG. 1C.
  • the manufacturing process of the composite material is as close as possible to the construction method in the civil engineering field. After pouring for 1 day, the mold is removed and then placed in the standard curing room for 28 days. After the curing, the composite material was placed under laboratory conditions for 7 days, dried naturally, and then packaged in a protected area.
  • the protection zone consists of five layers, which are Kraft Silicone Rubber - Insulation Tape - Epoxy Sealant - Insulation Tape - Epoxy Sealant. Firstly, apply a uniform layer of Kraft silicone rubber on the surface of the clean and dry composite board test piece protection surface, and dry it under laboratory conditions for 24 hours; then wrap it on the silicone rubber surface with insulating tape; then use the ring.
  • the oxygen sealant was solid-sealed and placed in a laboratory condition for 48 hours to be naturally cured; then it was wrapped with an insulating tape; finally, it was sealed with an epoxy sealant and allowed to cure under laboratory conditions for 48 hours.
  • the carbon fiber (experimental) recovery system device mainly comprises four parts: a DC power supply, providing a unidirectional working current for the system; a cathode and anode, the recovered sample is connected as an anode to the positive electrode of the power source, and the degraded cement-based colloid is consumed.
  • the stainless steel piece is connected as a cathode to the negative pole of the power source; the electrolyte includes different concentrations of NaCl base solution and catalyst HNO 3 ; the data log (Datalog) is connected in parallel with the recovered sample and the stainless steel piece to monitor the sample voltage change.
  • the recovered sample was placed in parallel with the stainless steel sheet and the distance was fixed at 50 m.
  • the experimental design mainly considers parameters including current density, NaCl concentration in solution, catalyst HNO 3 concentration, and temperature effects.
  • parameters including current density, NaCl concentration in solution, catalyst HNO 3 concentration, and temperature effects.
  • the second series of test parameters include: (1) two current values (20 mA, 40 mA), corresponding to two current densities (3333.3 mA / m2, 6666.7 mA / m2); (2) sodium chloride concentration of an electrolyte (2%); (3) one catalyst nitric acid concentration (3 g/L) and (4) three temperature gradients (40 ° C, 60 ° C and 75 ° C).
  • Six parameters can be obtained, each of which includes three parallel test pieces. The detailed test piece grouping and experimental parameters are shown in Table 2. It is worth noting that in order to achieve recovery at normal temperature and pressure, the maximum temperature set by the experiment is only 75 ° C, and the high temperature conditions are not considered.
  • the test piece number is determined by the action current intensity, NaCl concentration, HNO 3 concentration and temperature.
  • the test piece number is “I20S 2.0 H 3 T 40 ”.
  • the first part “I20” means that the constant current intensity applied by the test piece is 20 mA.
  • two-part “S2” refers to the concentration of the electrolyte is NaCl in deionized water 2% by mass of the third portion "H 3” refers to the concentration of HNO 3 per liter of the electrolytic solution was added 3g / L.
  • the fourth part "T40” means that the temperature of the electrolyte is kept at 40 °C during the experiment. Without the fourth part, the test is carried out at room temperature (temperature is 25 degrees)
  • the HIOKI-LR8400 data logger (Datalog) manufactured by Nissin Electric Co., Ltd. was used to collect data once per hour.
  • the frequency of the frequency is 1h/time and the power frequency is 50HZ.
  • the carbon fiber monofilament tensile strength test was carried out using a nano UTM 150 model nano-stretcher manufactured by Agilent, USA; the test system was UTM-Bionix Standard Toecomp Quasistatic.
  • the test parameters were set as follows: application load 750 ⁇ N, tensile rate 0.2 ⁇ m/s, load resolution 50 nN, displacement resolution ⁇ 0.1 nm, tensile resolution 35 nm, actuator maximum displacement 1 mm.
  • the test temperature is 20 ° C - 30 ° C, and the air humidity is 40%.
  • the carbon fiber monofilament Before the carbon fiber monofilament tensile test, the carbon fiber monofilament should be fixed on the photo paper of 15mm 20mm in size, and the middle of the photo paper is a circular hole with a diameter of 6mm. The carbon fiber monofilament is adhered to the horizontal diameter of the round hole by using the paste glue. On the fiber, the fiber should not be too tight or too loose.
  • the sample After the sample is prepared, it is placed in laboratory conditions for one day, and the glue is allowed to dry naturally.
  • the sample can be loaded into the nano-tensile fixture, then the edges of the photo paper are cut and the test begins.
  • the carbon fiber monofilament test length is 61 mm, the number of samples to be tested per sample is 20, and the carbon fiber monofilament strength result is 20 sample intensity average.
  • the tensile strength formula of the monofilament is as follows:
  • the diameter of the carbon fiber monofilament was measured using a laser caliper manufactured by Changchun Industrial Optoelectronic Technology Co., Ltd. The sample is placed on the sample holder, and the diffraction dark line spacing of the monofilament is measured by the diffraction principle.
  • the exact diameter of the monofilament can be calculated by formula conversion, and the formula is as follows:
  • the HM410 composite interface feature evaluation device manufactured by Japan Toyon Co., Ltd. was used for the droplet embedding test.
  • the test parameters were set as follows: the test speed was 0.12 mm/min, and the microscope magnification was 2 times.
  • the diameter of the test resin sphere should be selected from 40 ⁇ m to 80 ⁇ m.
  • the number of resin balls tested in each sample was 5, and the interfacial shear strength results were averaged.
  • the interface shear strength formula is as follows:
  • the surface morphology of the recovered carbon fiber was observed and analyzed by using the FINA company's Quanta TM 250FEG model scanning electron microscope. Select high vacuum mode, the working distance is about 10mm, and the test acceleration voltage is 20KV. In order to obtain a clearer and more accurate surface topography, it is necessary to increase the conductivity of the carbon fiber, so the sample is subjected to gold spray treatment in an ion sputtering apparatus before being tested.
  • the ICON-PT-PKG model scanning probe microscope produced by Bruker Company of USA was used to test the recovered carbon fiber to obtain two-dimensional and three-dimensional images of the surface topography and undulation.
  • the sample scanning range of this experiment was 4 ⁇ m, and the tapping mode was adopted, and the scanning rate was 1.0 Hz.
  • the length of the carbon fiber monofilament should not be less than 20 mm.
  • N y the number of steps in the Y axis
  • the D8Advance high-resolution X-ray analyzer manufactured by Bruker of Germany was used to scan and recover the recovered carbon fiber, and the crystal structure information of the surface component can be qualitatively obtained.
  • the working voltage is 40KV
  • the working current is 200mA
  • the test copper target radiation wavelength is 154mm
  • the scanning angle is 10° ⁇ 80°
  • the step size is 0.02°
  • the scanning time per step is 0.2S.
  • the phase analysis of the map was performed using Jade 5.0 software.
  • the ULVAC-PHI VPII model photoelectron spectrometer was used to perform the full-spectrum scanning of the recovered carbon fiber in the range of 0eV ⁇ 800eV to obtain the surface element information, and then the C1s were scanned with high resolution, and the results were performed by XPSPeak4.1 software. Gaussian function and Lorentz function fitting, analysis of the type and content of functional groups. When testing, it is necessary to ensure that the carbon fiber is placed flat on the test bench.
  • the X-ray source of the monochromator is an Al target, and the test elements include: C, O, Cl, N, Si, Ca, and 90° is selected as the incident angle.
  • the recycling process step mainly involves three parts: (A) placing the prepared carbon fiber reinforced cement-based composite material (plate) in the electrolyte; (B) energizing the carbon fiber reinforced cement-based composite material placed in the electrolyte, wherein the carbon fiber The reinforced cement-based composite material is connected to the positive electrode of the power source, and the current is controlled within a suitable size range; and (C) the electrification reaction is taken out from the electrolyte for a suitable time (usually 8-240 hours).
  • the current magnitude is controlled at 20 mA and 40 mA according to different groupings; the sodium chloride concentration (% by weight) is controlled at 2.0% and 3.0%; the catalyst HNO 3 concentration is controlled at 0%, 1 %, 3%, and 5%), a total of 16 groups of test samples.
  • Table 4.1 The sample number is determined by the current magnitude, NaCl concentration and catalyst HNO 3 concentration. For example, the sample number is “I20S 2.0 H 1 ”.
  • the first part “I20” means that the current applied by the sample is 20 mA, and the second part “S 2.0 ” refers to electrolysis.
  • the NaCl concentration in the liquid was 2.0%, and the third portion "H 1 " means that the concentration of HNO 3 added per liter of the electrolyte was 1 g.
  • the specific experimental parameters and grouping conditions are shown in Table 5.1.
  • the electrochemical recovery cycle was 8 days. After the recovery, the sample was taken out, the cement-based colloid on the surface was removed, and the obtained carbon fiber was washed and dried, and then subjected to various tests.
  • Example 5 Cleaning and removing the carbon fiber
  • the first series of experimental electrochemical recovery cycles was 8 days, and the second series of experimental electrochemical recovery cycles was 4 days.
  • the cement-based gel has a small amount of dissolution, and there are fine cementitious material particles in the solution and on the cathode of the stainless steel sheet.
  • the test piece was taken out from the liquid, and it was found that the inorganic glue was still connected to the carbon fiber, as shown in FIG. Therefore, the obtained carbon fiber recyclate is a mixture of carbon fiber and cement-based inorganic gum. In other words, the recovered carbon fiber is still joined to the cement-based inorganic glue.
  • the cement-based gel material becomes very soft and can be easily removed with a hard straight brush or a rigid plate.
  • a similar strong rejection may leave a layer of colloid on the surface of the carbon fiber that is difficult to remove.
  • a hole may be inserted every 0.1 mm or more on the surface of the carbon fiber recovery material, and then washed with a water flow of 0.1 MPa or more, and the scouring time is 3 seconds or more to remove the cement-based inorganic material. gum.
  • the resulting carbon fiber recyclate comprises carbon fibers and an inorganic gum, typically in the form of a plate or strip.
  • the hardness of the coated pencil hardness test method was tested.
  • the QHQ-A pencil hardness tester produced by AIPLI Instrument Co., Ltd. was selected and placed on the surface according to the specification GB/T6739-2006/ISO15184:1998 under the conditions of temperature (23 ⁇ 2) °C and relative humidity (50 ⁇ 5)%.
  • a uniform structure of the plate the pencil is pressed down on the surface of the composite at a 45° angle under a load of 750g, pushing 10mm away from the operator at a speed of 0.5mm/s to 1mm/s, from the pencil softest level 9B Initially, the cohesive failure visible to the surface of the composite was observed and the depth of failure was measured using a vernier caliper with an accuracy of 0.02 mm.
  • the detailed hardness grade of the tested composites is shown in Table 6.1.
  • the hard part refers to the part of the sample with hardness ⁇ 9H
  • the soft part refers to the part with hardness ⁇ 9H.
  • the hardness of the pencil hardness tester from low to high is: 9B-8B-7B-6B-5B-4B-3B-2B-1B-HB-FH-2H-3H-4H-5H-6H-7H-8H- 9H
  • the samples of I20S 2.0 H 1 and I40S 2.0 H 1 are still divided into hard and soft parts.
  • the hardness of the hard part is greater than 9H and 9H, respectively.
  • the hardness of the soft part is 5B and 9B respectively.
  • I20S 3.0 The sample hardness of H 1 and I40S 3.0 H 1 was 7B and 9B, respectively.
  • the above results show that the higher the NaCl concentration, the greater the softening of the carbon fiber reinforced cement-based composite sample, and the softer the hardness. Similarly, the carbon fiber reinforced cement-based composite sample is softer due to the increase in current.
  • the hardness of the H 3 and H 5 series samples is less than 9B, and the above conclusion can be obtained from the comparison of the depth of cohesive failure caused by the test.
  • FIG. 3A to 3D are SEM scan results of the carbon fiber recyclate, wherein FIG. 3A is the interface between the cement-based and carbon fiber of the carbon fiber reinforced cement-based material which has not been electrochemically recovered, and the rib groove The groove structure is quite complete and regular, and it can form a strong mechanical bite with carbon fiber. The interface has only very small holes, and no cracks and other defects are seen.
  • Fig. 3B is a partial enlargement (magnification 10000 times) at the box in Fig. 3A, from which a network structure in which the cement paste and the polymer are interlaced with each other can be found, which increase the strength and bonding property of the material itself. .
  • Fig. 3A is the interface between the cement-based and carbon fiber of the carbon fiber reinforced cement-based material which has not been electrochemically recovered, and the rib groove
  • the groove structure is quite complete and regular, and it can form a strong mechanical bite with carbon fiber. The interface has only very small holes, and no cracks and other defects
  • FIG. 3C shows the interface between the cement-based material and the carbon fiber of the carbon fiber recyclate in I40S 3.0 H 1 . It can be seen that the rhombic groove structure has been divided into broken small units by the large cracks in the longitudinal and lateral directions, and is in a fluffy shape. At the same time, there are many large crack pores distributed, the porosity is increased sharply, the interface has completely lost the mechanical bite cooperation with carbon fiber, and the adhesion is greatly reduced.
  • Figure D is a partial enlargement (magnification 10,000 times) at the box in Figure C. It can be seen that the inside of the crack is a white loose structure, the intercalated network structure of the cement paste and the polymer has been destroyed, and the cement-based material is hollowed out. The bond between the carbon fiber and the cement-based interface has been lost.
  • the carbon fiber precursor has a mass of 841 mg, and the carbon fiber cloth with a mass of 30 mm ⁇ 100 mm is weighed.
  • the H 0 series is recovered from the sample of the carbon fiber reinforced cement-based composite material.
  • the obtained carbon fiber recyclate has a large hardness and cannot easily remove the cement-based material without any effort, so it is defined as a carbon fiber recovery amount of 0 g/L, which is not listed in the table.
  • the amount of carbon fiber recovered from different group samples is different, and the amount of carbon fiber recovered between different groups is intuitive, as shown in Figure 4.
  • the carbon fiber recovery amount increases first and then decreases with the increase of HNO 3 concentration, and the carbon fiber recovery amount is the largest when the HNO 3 concentration is 3g/L.
  • the recovery of I20S 2.0 and I40S 2.0 was significantly lower, only 233 mg and 286 mg, because only the carbon fiber of the soft part was recovered, and the area of the soft part was relatively small in the recovery area.
  • the H 5 series samples have less carbon fiber recovery, mainly because the carbon fiber is more deteriorated, the surface layer is peeled off, and it becomes very fine and short hair, which adheres to the cement-based material and is also lost during the cleaning stage.
  • the I40 series carbon fiber recovery is generally lower than the I20 series, and the S 3.0 series carbon fiber recovery is lower than the S 2.0 (except when B is 1g/L), indicating that the larger current and larger sodium chloride concentration cause the carbon fiber to deteriorate more. . Not conducive to carbon fiber recycling.
  • CB indicates that the failure mode is the interface peeling damage between carbon fiber and inorganic grease
  • Carbon fiber reinforced cement-based composites have some differences before and after soaking, the color becomes lighter, and some small holes appear on the surface.
  • the hardness test is carried out, and the results are shown in Table 6.3. It can be seen from the table that the hardness of the treated composite is still very high. When the concentration of HNO 3 reaches 10g/L, the hardness of the composite is 3B. The cement colloid can not be removed without the aid of mechanical tools, and the concentration is high for a long time.
  • the catalyst B (HNO 3 ) solution is soaked, the carbon fiber properties are greatly deteriorated. It indicates that current plays an important role in the softening of carbon fiber reinforced cement-based composites, and electrochemical treatment is more effective in conforming with materials.
  • the voltages of all samples remained substantially stable during the electrochemical recovery cycle without significant fluctuations.
  • the sample voltages of different groups are different.
  • the H 0 (0g/L) group has the highest voltage and the highest relative fluctuation. The reason may be that the catalyst HNO 3 has a slower softening effect on the carbon fiber reinforced cement matrix composite sample and the porosity is very small. The conductivity of the sample is not good, so the voltage is high and the fluctuation is large.
  • the voltage of the H 5 series sample is lower than the H 0 series, but it is still relatively high. In the H 5 series, the damage of the sample cement-based material is very serious and has been applied to the carbon fiber. The higher voltage may be caused by the deterioration of the carbon fiber and the increase in resistance. Big related.
  • the sample voltages of H 3 (3g/L) and H 1 (1g/L) groups are lower, which is due to the milder effect of electrochemical action on carbon fiber reinforced cement-based composites, the deterioration of carbon fibers is slight, and the electrical conductivity is better.
  • the I40 series sample voltage is larger than the I20 series
  • the S 3.0 series sample voltage is larger than the S 2.0 series, indicating that the larger the voltage and the NaCl concentration, the larger the resistance value, and thus the higher the voltage.
  • the diameter of the recovered carbon fiber does not change, indicating that although the carbon fiber undergoes electrochemical oxidation and acid corrosion during the electrochemical recovery process, there is substantially no peeling of the surface of the carbon fiber.
  • the tensile strength of the monofilament of the carbon fiber precursor was 3588 MPa, and the tensile strength of I20S 2.0 H 1 in the recovered carbon fiber was 3072 MPa, which was 85.62% of the carbon fiber precursor; the tensile strength of I40S 3.0 H 5 was the lowest. 2162MPa, only 60.26% of carbon fiber precursor.
  • the tensile strength of the monofilament of other recycled carbon fibers showed a different degree of decline compared to the carbon fiber precursor, as shown in Figure 6.
  • the recycled carbon fiber resulting single filament tensile strength with increasing concentration of HNO 3 decreased tensile strength in 0 ⁇ 3 (g / L) concentration of HNO 3 in section, of carbon fibers
  • the decrease is small, and the tensile strength of carbon fiber in the range of HNO 3 concentration of 3 to 5 (g/L) drops sharply, indicating that the higher the concentration of HNO 3 , the more serious the deterioration of carbon fiber, especially when the concentration of HNO 3 exceeds 3 (g). /L) After.
  • the concentration of HNO 3 is 1 (g/L) and 3 (g/L)
  • the difference in tensile strength between carbon fibers under different parameters is not large, and the tensile strength of H 1 series carbon fibers is between 2987 MPa and 3072 MPa.
  • the tensile strength of 3 series carbon fiber ranges from 2898MPa to 2974MPa.
  • the tensile strength of I20 series carbon fiber is higher than that of I40 series.
  • the tensile strength of S 2.0 series carbon fiber is higher than that of S 3.0 ; when the concentration of HNO 3 is 5 (g/L) At the same time, the difference in the strength of the carbon fiber between the different parameters is relatively small, but the sample of the small current series is still higher than the sample of the high current series, and the sample of the low sodium chloride concentration is higher than the sample of the high concentration series.
  • the interfacial shear strength of carbon fiber precursor and inorganic grease is 27.09 MPa
  • the failure mode is DB
  • the interfacial shear strength of the recovered carbon fiber is large, except for the H 5 series, other series of sample shearing
  • the strength is greater than or equal to the carbon fiber precursor
  • the failure mode is related to the HNO 3 concentration
  • the failure mode of the H 1 series sample is DB
  • the destruction mode of the H 3 series sample is CB
  • the failure mode of the H 5 series sample is EB, with the concentration of HNO 3
  • CB indicates that the failure mode is the peeling failure of the interface between carbon fiber and epoxy resin
  • the interfacial shear strength of the recovered carbon fiber decreases with the increase of the HNO 3 concentration, but the carbon fiber recovered by the H 1 and H 3 series is larger than the shear strength of the original yarn, indicating that it is at a lower concentration. Electrochemical oxidation under B conditions can increase the shear strength.
  • the carbon fiber precursor has a failure mode of DB, the inorganic lipid layer is peeled off, and the surface of the carbon fiber is bonded with a smooth resin;
  • Figs. 8B and 8C are I20S 2.0 H 1 and I40S 2.0 H 1 , respectively.
  • the acicular resin not only increases the surface area of the fracture, but also acts like a steel rib, greatly improves the mechanical bite force and increases the adhesion to the inorganic grease. Knot performance, so the shear strength of the S 2.0 series samples is still higher than that of carbon fiber strands.
  • concentration of HNO 3 is 1 (g/L) and 3 (g/L)
  • the shear strength of I20 series samples is higher than that of I40 series, I20S 3.0 H 1 ;
  • the shear strength of S 2.0 series samples is higher than that of S 3.0 series;
  • the shear strength of the sample with small current and low B concentration is greater, but due to excessive oxidation etching, the influence of current and B parameters on shear strength is very small.
  • the surface topography of carbon fiber plays a very important role in the interfacial adhesion properties. It is characterized by roughness and morphology structure.
  • the AFM scanning test results of carbon fiber precursor and recovered carbon fiber are shown in Table 7.1 and Figure 10, respectively. It should be noted that the recycled carbon fibers of the S 2.0 series and the S 3.0 series have little difference in roughness and morphology, so only the carbon fiber AFM images recovered by the S 2.0 series are listed here.
  • the surface of the carbon fiber precursor is very smooth, has no longitudinal groove structure, has almost no skin convex structure, and has a calculated roughness of 144 nm.
  • Fig. 10C to Fig. 10F it can be found that in the H 1 carbon fiber series, due to the oxidative etching action of the recycling process, a significant longitudinal groove structure and a skin convex structure appear on the surface of the carbon fiber, and these fine structures function like steel ribs.
  • the roughness of I20S 2.0 H 1 and I40S 2.0 H 1 are 180nm and 178nm respectively, increase the specific surface area, improve the wettability and improve the interface. Bonding properties, therefore, the shear strength of the carbon fiber recovered from the H 1 series is much higher than that of the carbon fiber precursor. It can be seen from Fig. 10G to Fig. 10J that when the concentration of HNO 3 is increased to 3, the surface of the carbon fiber still has a longitudinal groove structure, but is weaker than the H 1 series, and the convex structure on the surface of the I20S 2.0 H 3 carbon fiber is increased, and the I40S 2.0 is increased.
  • H 3 has only different longitudinal groove structures, and the calculated roughness is 208 nm and 162 nm, respectively.
  • the longitudinal groove structure becomes weak, resulting in a decrease in the mechanical bite of the carbon fiber surface. Therefore, the shear strength of the carbon fiber interface recovered by the H 3 series is obtained. It is lower than the H 1 series, but still higher than the carbon fiber precursor, indicating that the concentration of HNO 3 is increased, causing the carbon fiber to undergo oxidative etching and the like to be deteriorated, resulting in weakened interface shear strength. It can be seen from Fig. 10K to Fig.
  • the longitudinal groove structure is hardly visible on the surface of the I20S 2.0 H 5 and I40S 2.0 H 5 carbon fibers, and only the miscellaneous convex structure is obtained, and the calculated roughness is obtained.
  • the degrees are 104 nm and 121 nm, respectively. It should be noted that the longitudinal grooves of the I40S 2.0 H 5 are produced during production, not by oxidative etching. Excessive oxidative etching causes the activated carbon particles to fall off, and the longitudinal groove structure cannot be formed.
  • the mechanical bite force of the carbon fiber drops sharply, resulting in a decrease in the shear strength of the carbon fiber recovered by the H 5 series, slightly lower than that of the carbon fiber precursor, and severely oxidized.
  • the adhesion between the convex mechanism and the carbon fiber body is weakened, and peeling is likely to occur when the resin droplets are dialed out, resulting in an EB failure mode.
  • the above shows that when the concentration of HNO 3 is low, the small amount of oxidative etching in the electrochemical recovery process increases the interfacial shear strength of the carbon fiber, and when the concentration of HNO 3 increases to a certain extent, the excessive oxidation etching causes the carbon fiber to The interface shear strength is reduced.
  • the XPS scanning full spectrum and the C1s high resolution narrow spectrum of the recovered carbon fiber are shown in Fig. 11A to Fig. 11H, and the left column is the scanning full spectrum of the sample. It can be seen from the scanning full spectrum that there are five main peaks in the figure, namely two main peaks: C (284.6 eV) and O (532.0 eV); three secondary peaks: Si (99.5 eV), Cl (199.8 eV). ) and Ca (347eV).
  • the basic elements of the carbon fiber precursor are carbon and oxygen, and the small amount of silicon, chlorine and calcium detected is introduced during the experiment.
  • the specific chemical element content of the carbon fiber surface recovered from the VCF and I20S 2.0 groups is shown in Table 7.2.
  • the carbon fiber surface has a carbon content of 79.3% and an oxygen content of 20.7%, and no other element content is detected.
  • the carbon content of all recovered carbon fiber surfaces is relatively close, which is about 10% lower than that of carbon fiber precursors, and the oxygen content is increased to some extent. From the oxygen-carbon ratio, the recovered carbon fibers are much higher than the carbon fiber precursors. 0.2610, in the three HNO 3 concentration gradients, H 3 has the highest oxygen-to-carbon ratio, followed by H 5 , and the lowest is H 1 , indicating that H 3 is the optimal concentration in the region and can introduce more oxygen to obtain a larger Surface activity enhances the chemical bonding ability with inorganic lipids.
  • the C1s peak fitting is shown in the right column of Figure 5.15. It should be noted that the C1s of the carbon fiber precursor is double-peak and there is no area after the 288eV peak, so the fitting results show that the surface of the carbon fiber precursor does not contain O.
  • the oxygen-carbon ratio and functional group content of the recovered carbon fiber showed that the degree of oxidation of carbon fiber was too low when the concentration of HNO 3 was 1.0 g/L.
  • the concentration of HNO 3 was 3.0 g/L, the degree of oxidation of carbon fiber was the best, and HNO was increased.
  • the XRD spectrum is basically higher in temperature, the higher the diffraction intensity of the characteristic peak, the sharper the peak, indicating that the higher the recovery temperature, the better the crystallinity of carbon fiber and the smaller the crystal grain.
  • Papirer E's research shows that the smaller the surface of carbon fiber, the more unsaturated C atoms on the surface edges and edges, the higher the surface activity, which can improve the bonding performance of carbon fiber and resin to some extent, and improve the pulling of carbon fiber. Stretch strength.
  • the I20 series carbon fiber has better characteristic peak than the I40 series, indicating that the small current effect has less influence on the graphite block structure of the carbon fiber, and is more conducive to recovering the mechanical properties of the carbon fiber.
  • the chemical reaction process for the recovery of carbon fibers by electrochemical methods should also have suitable reaction conditions.
  • the present invention determines the appropriate temperature for the electrochemical recovery process of the present invention by the following experimental results. Similarly, multiple sets of samples (shown in Table 6.1 below) were used to test the appropriate reaction temperatures, with current intensities of 20 mA and 40 mA, NaCl concentration of 2.0 (%), and HNO 3 dose of 3.0 g/L.
  • the temperature gradient is a total of 6 sets of four temperature gradients that exclude extreme temperatures of extremely low yields (very low, such as below 0 ° C, and temperatures above 100 ° C).
  • the sample number is determined by the action current, NaCl concentration, catalyst HNO 3 concentration and temperature gradient, such as the sample number “I20S 2.0 H 3 T 40 ”.
  • the first part “I20” means the current applied by the sample is 20 mA
  • the second part “S 2.0” refers to the electrolyte concentration of 2.0% NaCl
  • part III" H 3 means that the catalyst is added to the electrolyte concentration of HNO 3 is 3.0g / L.
  • the fourth part “T 40” means that the temperature of the electrolyte is maintained at 40 ° C during the experiment.
  • Table 8.1 Detailed experimental groupings and experimental parameters are shown in Table 8.1.
  • the electrochemical recovery period of this part was 4 days. After the recovery, the composite was tested for hardness. The cement-based colloid of the composite is then removed and the carbon fibers are removed. The recovered carbon fiber obtained is washed and dried, and various tests are performed. After testing, the recovered carbon fiber still maintains a tow shape with a length of about 100 mm, which is basically the same as the sample recovery length, and the surface is lustrous, indicating that the carbon fiber is less damaged by oxidation and corrosion during the recovery process.
  • the hardness of the pencil hardness tester from low to high is: 9B to 8B to 7B to 6B to 5B to 4B to 3B to 2B to 1B to HB to F to H to 2H to 3H to 4H to 5H to 6H to 7H ⁇ 8H ⁇ 9H
  • the recovery of carbon fiber showed a high first and then low trend with increasing temperature.
  • T 40 40 ° C
  • the carbon fiber recovery was the largest, and the recovery of I20S 2.0 H 3 T 40 was 772 mg. , reaching 91.8% of the carbon fiber precursor.
  • the recovery cycle at high temperature is only half of the normal temperature (T 0 , 25 ° C)
  • the recovery of carbon fiber is higher. The reason is that the shorter the electrochemical oxidation time of the carbon fiber, the lower the degree of deterioration, and the more the resulting filament Less, so the amount recovered is more.
  • the carbon fiber recovery of I20 series samples is obviously higher than that of I40 series, especially in the high temperature stage.
  • I40 series carbon fiber has more filaments, not only more cemented on cement-based gel, but also a part of The water flow washed away, indicating that the deterioration of the carbon fiber caused by the large current is more serious.
  • CB indicates that the failure mode is the interface peeling damage between carbon fiber and inorganic grease
  • the carbon fiber diameter remains unchanged at 7 ⁇ m, indicating that the electrochemical oxidation and acid corrosion of the carbon fiber during the electrochemical recovery process are less severe, and there is substantially no peeling of the surface of the carbon fiber.
  • the tensile strength of I20S 2.0 H 3 T 3 is up to 3,214 MPa, which is 89.58% of the carbon fiber precursor; the tensile strength of I40S 2.0 H 3 T 1 is 2,881 MPa, which is 80.30 of the carbon fiber precursor. %.
  • the tensile strength of the monofilament of other recycled carbon fibers is lower than that of the carbon fiber precursor.
  • the relationship between the tensile strength of the monofilament and the temperature gradient is shown in Fig. 14.
  • the tensile strength of the monofilament of the recovered carbon fiber showed a tendency to decrease first and then to rise slowly with an increase in temperature. It should be pointed out that under normal temperature T 0 (25 ° C), the recovery period of carbon fiber is 8 days. Under high temperature conditions, the recovery period is shortened to 4 days, and the carbon fiber is weakened by oxidation and corrosion, so the damage is relatively small. The tensile strength of carbon fiber is naturally higher. However, at a temperature of T 1 (40 ° C), the tensile strength of the carbon fiber is lower than that at T 0 , and the carbon fiber should be subjected to some type of more serious deterioration damage at this temperature. The tensile strength of the I20 series sample is higher than that of the I40 series, and as the temperature increases, the difference between the two increases continuously. It may be that under high temperature conditions, the large current makes the oxidation reaction rate of the sample faster.
  • the destruction mode of the recovered carbon fiber except for I40S 2.0 H 3 T 2 is CB, and the failure modes of other samples are all DB.
  • the interfacial shear strength of I20S 2.0 H 3 T 2 is up to 28.45 MPa, which is 105.02% of the carbon fiber precursor.
  • the interfacial shear strength of other samples is different compared with the carbon fiber precursor.
  • CB indicates that the failure mode is the peeling failure of the interface between carbon fiber and epoxy resin
  • the interfacial shear strength of the recovered carbon fiber increases first and then increases and then decreases with the increase of temperature.
  • the high shear strength of the high temperature sample is higher than that of the normal temperature T 0 sample. The reason may be that the recovery period of the high temperature sample is only Half of the sample at room temperature is related to the low degree of fine structure of the surface which is oxidized and etched, and the roughness is low.
  • the fracture interface of I20S 2.0 H 3 T 1 and I40S 2.0 H 3 T 1 is a smooth inorganic lipid layer with low shear strength of 22.78 MPa and 23.51 MPa, respectively. 84.09% and 86.78% of the silk.
  • the failure modes of I20S 2.0 H 3 T 2 and I40S 2.0 H 3 T 2 are DB and CB, respectively, and the rupture interface is bonded with a lot of acicular elongated inorganic grease, and these acicular resins can The damaged surface area is increased, which acts like a steel crescent rib, which greatly improves the mechanical bite force, so the shear strength of the sample is improved, reaching 105.02% and 98.74% of the carbon fiber precursor, respectively.
  • the failure modes of I20S 2.0 H 3 T 3 and I40S 2.0 H 3 T 3 are both DB, the inorganic lipid layer is destroyed, and a small amount of acicular inorganic lipid can be observed at the destruction interface.
  • the strength is higher, which is 92.69% and 89.66% of the carbon fiber precursor, respectively.
  • FIG carbon fiber series T 1 is recovered 18A to 18D, the etching degree of oxidation less recovery process, the longitudinal grooves of the surface structure of the carbon fiber shallow, raised structures size between about 20 ⁇ m ⁇ 50 ⁇ m, I20S 2.0 H 3
  • the roughness calculated by T 1 and I40S 2.0 H 3 T 1 is 134 nm and 149 nm, respectively, which is not much different from the roughness of 144 nm of the carbon fiber precursor. Therefore, the interfacial shear strength of the recovered carbon fiber is not high.
  • Figure 18E to Figure 18H the surface of the I40 carbon fiber series has a deeper longitudinal groove structure with a larger width.
  • the surface of the I40S 2.0 H 3 T 2 is densely convex.
  • the size of these raised structures is about 100 nm ⁇ between 300nm, I20S 2.0 H 3 T 2 and I40S 2.0 H 3 T 2 roughness 168nm and 169nm, respectively, longitudinal grooves and projections carbon fiber structure to improve the mechanical bite force, the specific surface area to improve wettability, and therefore T
  • the shear failure interface of the 2 series carbon fiber can bond the needle-like resin, which greatly improves the interfacial shear strength of the carbon fiber.
  • Fig. 19A to Fig. 19F After scanning, the scanned full spectrum of the recovered carbon fiber and the high resolution narrow spectrum of C1s are shown in Fig. 19A to Fig. 19F.
  • the left column is the full spectrum of the sample, and the right column is the corresponding high resolution narrow spectrum of C1s and its peak resolution.
  • Figure. It can be seen from the scanning full spectrum that there are six main peaks in the figure, namely two main peaks: C (284.6 eV) and O (532.0 eV); four secondary peaks: Si (99.5 eV), Cl (199.8 eV). ), Ca (347 eV) and N (399.5 eV).
  • the basic elements of the carbon fiber precursor are carbon and oxygen, and the small amount of silicon, chlorine, calcium and calcium detected is introduced during the experiment. See Table 8.7 for the chemical element content of the carbon fiber obtained by the recovery of different temperature gradients.
  • the recycled carbon fiber has a certain decrease in the content of C element compared with the carbon fiber precursor, and the oxygen content increases significantly.
  • the carbon fiber precursor is only 0.2610.
  • the lowest oxygen-to-carbon ratio of I20S 2.0 H 3 T 3 also reached 0.4066, which is more than 1.5 times that of the carbon fiber precursor. This indicates that more carbon is introduced into the surface of the recovered carbon fiber, and more activity is obtained.
  • the oxygen-to-carbon ratio of I20S 2.0 H 3 T 2 is 0.4281, I20S 2.0 H 3 T 1 is slightly lower, the oxygen-carbon ratio is 0.4252, and I20S 2.0 H 3 T 3 is the lowest.
  • the oxygen-carbon ratio of I20S 2.0 H 3 T 0 is 0.3859, which indicates that although the recovery period shortens and the oxidation time of carbon fiber becomes shorter, the high-temperature condition causes the oxygen introduction amount on the surface of carbon fiber to be larger.
  • the surface oxygen of carbon fiber The carbon ratio is the largest and then begins to decline.
  • chlorine is introduced into the surface of the carbon fiber, and the chlorine content decreases as the temperature increases.
  • I20S 2.0 H 3 T 2 and I20S 2.0 H 3 T 3 surface of carbon fibers also introduces a small amount of nitrogen, silicon, and calcium.
  • the C1s peak fitting is shown in the right column of Figure 6.9.
  • the specific recovered carbon fiber surface functional group content is shown in Table 8.8.
  • the crystallinity of the recovered carbon fibers is relatively poor.
  • the diffraction peak intensity of H 1 series recycled carbon fiber is low.
  • concentration of nitric acid increases to 3g/L
  • the intensity of the diffraction peak increases, and the peak becomes sharper.
  • concentration of nitric acid continues to increase to 5g/L
  • the diffraction peak The strength of the peak decreases, and the peak end becomes smooth, indicating that the crystallinity of the carbon fiber of the H 3 series is relatively good, and the concentration of nitric acid which is too high or too low causes the graphite block structure of the carbon fiber to be greatly affected in the recovery process.
  • the electrolyzer used may be various electrolytic cells, electrolytic cells, and the like which are well known in the art.
  • the above electrolysis device as a recovery container is provided with a chemical solution in which a pre-designed recyclant and a catalyst are mixed, which can effectively invade the cement-based cementing material of the carbon fiber reinforced cement-based composite material to be recovered, and destroy the chemical bond thereof. Promote the decomposition of cement-based cementitious materials.
  • the chemical solution includes, but is not limited to, water, HNO 3 (nitric acid), liquid ethanol, liquid ethylene glycol, various acidic solutions (including but not limited to H 2 Si 3 (metasilicate), HCN (hydrocyanic acid).
  • H 2 C 3 carbonic acid
  • HF hydrofluoric acid
  • C 3 COOH also known as C 2 H 4 O 2 acetic acid, also known as acetic acid
  • H 2 S hydrogen sulfuric acid
  • HClO hypoochlorous acid
  • HNO 2 nitrogen acid
  • all organic acids H 2 S 3 (sulfurous acid), etc.
  • various alkaline solutions including but not limited to potassium hydroxide solution, sodium hydroxide solution, etc.
  • various Chloride solution including but not limited to sodium chloride solution, zinc chloride solution, etc.
  • the above chemical liquid is characterized by being a mixed solution of the above various solutions, and the concentration of each solution is 0.001% to 99.9%
  • the carbon fiber material in the carbon fiber reinforced cementitious composite material to be recovered is connected to the positive electrode of the power source in a well-known manner during the energization process to ensure stable operation of the circuit during the recovery process.
  • the method of joining the fiber material to the positive electrode of the power source includes, but is not limited to, dissolving the resin, grinding away the resin, etc., to expose the inner fiber material to facilitate circuit connection.
  • the cathode material during energization is a well known conductive material including, but not limited to, steel, iron, various metals, various forms of graphite materials.
  • the current density is characterized by cooperating with the chemical solution to promote the solution of the cement-based cementitious material in the carbon fiber reinforced cement-based composite material to be recovered, without affecting each of the recovered carbon fibers.
  • the magnitude of the current density is calculated according to the surface area of the carbon fiber reinforced inorganic (cement-based) composite material in which the carbon fiber material is immersed in the electrolyte, and ranges from 3333.3 to 6666.7 mA/m 2 .
  • the energization time is characterized in that, in combination with the above chemical solution and current, the cement-based cementitious material in the carbon fiber reinforced cement-based composite material to be recovered can be decomposed without affecting the recycled carbon fiber.
  • the energization time is from 0.5 to 200 hours, preferably from 2 to 120 hours, more preferably from 4 to 48 hours.
  • various resin aging methods well known in the art can be used to speed up the recovery, such as ultraviolet ray strengthening, ultrasonic strengthening, and microwave strengthening.
  • the reaction temperature is from 25 ° C to 75 ° C, preferably from 40 ° C to 75 ° C, more preferably from 60 ° C to 75 ° C.
  • the pressure in the recovery container is adjusted to a preset size, which, together with the above chemical solution, current and temperature, causes expansion and decomposition of the cement-based cementitious material in the carbon fiber reinforced cement-based composite material to be recovered. At the same time, it does not affect the various mechanical properties, electrical conductivity, adhesion to resin materials and reworkability of recycled carbon fibers.
  • the pressure ranges from 0.5 to 20 atm and the pressurization time is from 0.5 to 200 hours.
  • the distance between the anode and the cathode material has an effect on the recovery effect, the recovery rate, and the recovery cost, and is preferably from 1 mm to 1000 mm, and more preferably from 20 mm to 60 mm.
  • the carbon fiber is taken out and stored, and then it can be put into production.
  • the method of removal is a variety of well known methods including, but not limited to, ultrasound, drying, heating, and the like, as well as combinations of various methods.
  • the length of the recovered carbon fiber is an important factor in its reuse value.
  • the carbon fiber recovered is straightened, and the length of the carbon fiber is about 80 mm to 100 mm.
  • the length of the sample recovery part of the experimental design is 100 mm. Considering the length loss of the carbon fiber obtained by the shear recovery, It is known that there is substantially no loss in the length of the carbon fiber during the electrochemical recovery process, indicating that the damage caused by the electrochemical oxidation of the carbon fiber is very slight throughout the recovery process.
  • the electrolyte solution contains 1 g/L to 5 g/L of catalyst B, wherein the catalyst B is a soluble acid, which may be But not limited to HNO 3 .
  • the amount of carbon fiber recovered from different carbon fiber reinforced cement-based composite samples is different, and the amount of carbon fiber recovered increases first and then decreases with the increase of HNO 3 concentration.
  • HNO 3 At a concentration of 3 g/L, the amount of carbon fiber recovered is the largest.
  • the concentration of HNO 3 is preferably controlled at 1 to 3 (g/L), and more preferably controlled at 3 g/L, whereby an ideal recovery effect can be obtained.

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  • Environmental & Geological Engineering (AREA)
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Abstract

A method for recovering high-performance carbon fiber from an inorganic cementing material, comprising the following steps: (A) placing a carbon fiber-reinforced inorganic (cement-based) composite material in an electrolyte at a reaction temperature of 25°C-75°C, the electrolyte containing 0.5%-3% by weight percent of NaCl and 1.0 g/L-5 g/L of a catalyst; (B) energizing the carbon fiber-reinforced cement-based composite material placed in the electrolyte, the carbon fiber reinforced cement-based composite material connecting to a positive electrode of a power source, and controlling the current density to be 3333.3-6666.7 mA/m2; and (C) after reacting by energizing for 0.5-200 hours, extracting a produced carbon fiber recovered product from the electrolyte.

Description

自无机胶凝材料中回收高性能碳纤维的方法Method for recovering high performance carbon fiber from inorganic cementitious material 技术领域Technical field
本发明涉及碳纤维的回收和再利用,尤其涉及一种自无机胶凝材料中回收高性能碳纤维的方法。The present invention relates to the recovery and reuse of carbon fibers, and more particularly to a method for recovering high performance carbon fibers from inorganic cementitious materials.
背景技术Background technique
碳纤维具有拉伸强度大、杨氏模量高、腐蚀抵抗性强、惰性氛围耐超高温、电磁波屏蔽性优异、生物相容性好和柔软可塑性强等优点。碳纤维制备技术经过半个多世纪的发展,发展了种类繁多的碳纤维原料,比如黏胶碳纤维、聚丙烯腈纤维(PAN)、沥青纤维、聚苯并咪唑纤维和聚酯纤维等。Carbon fiber has the advantages of high tensile strength, high Young's modulus, strong corrosion resistance, inert atmosphere resistance to ultra high temperature, excellent electromagnetic wave shielding, good biocompatibility and soft plasticity. After more than half a century of development, carbon fiber preparation technology has developed a wide variety of carbon fiber materials such as viscose carbon fiber, polyacrylonitrile fiber (PAN), asphalt fiber, polybenzimidazole fiber and polyester fiber.
碳纤维增强树脂基复合材料(Carbon Fiber Reinforced Plastic,CFRP)是以碳纤维作为增强体,有机环氧树脂为基体制作而成的复合材料。CFRP具有自重轻、耐腐蚀、抗拉强度高等优点,在航空航天、工业制造和体育用品等领域应用越来越广。2012年,世界范围内的碳纤维需求量为4.35万吨,预测2020年将达到13万吨。Carbon Fiber Reinforced Plastic (CFRP) is a composite material made of carbon fiber as a reinforcement and an organic epoxy resin as a matrix. CFRP has the advantages of light weight, corrosion resistance and high tensile strength, and it is widely used in aerospace, industrial manufacturing and sporting goods. In 2012, the world's carbon fiber demand was 43,500 tons, and it is predicted to reach 130,000 tons in 2020.
在土木工程领域,CFRP可采用有机环氧树脂胶凝材料固化后,粘贴或布置在结构表面或内部,提高结构承载力。环氧树脂胶含有多种极性基团和活性很大的环氧基,同时环氧固化物的内聚强度也很大,所以其胶接强度很高。但由于环氧树脂胶耐老化、耐腐蚀、耐湿热性能较差,抗剥离、抗开裂、抗冲击性能也不高,从上世纪90年代开始,土木工程中也采用无机胶凝材料,例如各种改性水泥净浆、砂浆和/或混凝土等水泥基材料、或碱基发材料等,粘结CFRP,形成碳纤维增强无机(水泥基)复合材料,进而加固建筑结构。无机胶凝材料具有腐蚀抵抗性能优良、强度高与韧性强等优异力学性能,与水泥或混凝土等传统土木工程结构材料粘结较好,因此加固材料(CFRP)与原结构可以共同工作,加固性能更好。In the field of civil engineering, CFRP can be cured by organic epoxy resin cementing material, pasted or placed on the surface or inside of the structure to improve the structural bearing capacity. The epoxy resin gel contains a plurality of polar groups and an active epoxy group, and the epoxy cured product has a large cohesive strength, so the bonding strength is high. However, due to the aging resistance, corrosion resistance and heat and humidity resistance of epoxy resin, anti-stripping, anti-cracking and impact resistance are not high. Since the 1990s, inorganic cementing materials have also been used in civil engineering, such as Cement-based materials such as modified cement paste, mortar and/or concrete, or base hair materials, etc., are bonded to CFRP to form a carbon fiber-reinforced inorganic (cement-based) composite material, thereby reinforcing the building structure. The inorganic cementitious material has excellent mechanical properties such as excellent corrosion resistance, high strength and toughness, and is well bonded to traditional civil engineering structural materials such as cement or concrete. Therefore, the reinforcing material (CFRP) and the original structure can work together and the reinforcing performance. better.
然而,CFRP等高性能纤维复合材料在土木工程领域的广泛应用,也带来了极其严重的建筑废弃物处理问题。同时,高性能纤维增强复合材料在寿命终结期后仍然保持良好的性能,经济价值较高,实现高性能纤维增强复合材料回收与再利用具有重要经济价值和社会意义。但是,采用水泥基胶凝材料结构加固用的CFRP在拆除后,碳纤维材料的建筑垃圾上会附着有很难剥离的水泥等无机材料,处理难度更大。However, the wide application of high-performance fiber composite materials such as CFRP in the civil engineering field has also brought about extremely serious construction waste disposal problems. At the same time, high-performance fiber reinforced composites still maintain good performance after the end of life, and have high economic value. It is of great economic and social significance to realize the recovery and reuse of high-performance fiber reinforced composite materials. However, after the CFRP used for the reinforcement of the cement-based cementitious material structure is removed, the inorganic waste material such as cement which is difficult to peel off adheres to the construction waste of the carbon fiber material, and the treatment is more difficult.
关于纤维增强复合材料废弃物的回收与应用研究,已经有大量学者与机构参与,国外特别是欧美和日本等发达国家凭借其产业和技术的先行优势,很早就开始进行纤维增强 复合材料废弃物的回收与再利用研究。然而,现有的各种碳纤维回收方法,都是针对以环氧树脂胶为基体材料和胶凝材料的,而针对碳纤维增强无机复合材料的碳纤维回收研究目前尚未有公开报导。Regarding the research on the recovery and application of fiber reinforced composite waste, a large number of scholars and institutions have participated in it. Foreign countries, especially Europe, the United States and Japan, have begun to carry out fiber reinforced composite wastes with the advance of their industries and technologies. Recycling and reuse research. However, various existing carbon fiber recovery methods are directed to epoxy resin adhesives as the matrix material and cementitious materials, and carbon fiber recovery studies for carbon fiber reinforced inorganic composite materials have not been publicly reported.
鉴于此,本发明提供一种技术可行、操作简便和经济效益高,同时兼顾环境保护的自无机胶凝材料中回收高性能碳纤维的方法,不仅有利于碳纤维材料的回收再利用,还可以解决建筑垃圾的处理问题,具备重要的经济价值和社会意义。In view of this, the present invention provides a method for recovering high-performance carbon fiber from inorganic cementitious materials which is technically feasible, simple in operation, high in economic efficiency and environmental protection, and is not only beneficial for recycling and reuse of carbon fiber materials, but also can solve construction. The problem of garbage disposal has important economic and social significance.
发明内容Summary of the invention
本发明的主要目的在于其提供一种自无机胶凝材料中回收高性能碳纤维的方法,其中本发明提供的该碳纤维回收方法具有工艺步骤简单、难度低、回收率高、成本低和纤维损伤小等优点。The main object of the present invention is to provide a method for recovering high-performance carbon fiber from an inorganic cementing material, wherein the carbon fiber recycling method provided by the invention has the advantages of simple process steps, low difficulty, high recovery rate, low cost and low fiber damage. Etc.
本发明的另一目的在于其提供一种自无机胶凝材料中回收高性能碳纤维的方法,其中本发明提供的该碳纤维回收方法不仅能够回收碳纤维,还能够同时回收树脂材料,并分解无机胶凝材料,从而减小含CFRP的建筑垃圾处理难度,并更大限度地使碳纤维增强水泥基复合材料废弃物得到回收和再利用,具有重大环保价值和重要社会意义。Another object of the present invention is to provide a method for recovering high-performance carbon fibers from an inorganic cementing material, wherein the carbon fiber recovery method provided by the present invention can not only recover carbon fibers, but also simultaneously recover resin materials and decompose inorganic gelation. Materials, in order to reduce the difficulty of handling construction waste containing CFRP, and to maximize the recycling and reuse of carbon fiber reinforced cement-based composite waste, have significant environmental value and important social significance.
本发明的另一目的在于其提供一种自无机胶凝材料中回收高性能碳纤维的方法,其中本发明提供的该碳纤维回收方法的所需化学试剂毒性小、对生产设备的要求低、反应条件温和。本发明提供的该碳纤维回收方法无需对碳纤维增强复合材料进行剪切和/或破碎处理,因此,可以对任意尺寸的材料进行回收。同时,无需对碳纤维增强复合材料进行剪切和/或破碎处理,也使得回收得到的碳纤维材料的力学性能几乎未收到任何损伤,回收得到的碳纤维材料的经济价值更高。Another object of the present invention is to provide a method for recovering high-performance carbon fibers from an inorganic cementing material, wherein the carbon fiber recovery method provided by the present invention has low toxicity, low requirements on production equipment, and reaction conditions. mild. The carbon fiber recovery method provided by the present invention does not require shearing and/or crushing treatment of the carbon fiber reinforced composite material, and therefore, materials of any size can be recovered. At the same time, it is not necessary to shear and/or crush the carbon fiber reinforced composite material, and the mechanical properties of the recovered carbon fiber material are hardly damaged, and the economic value of the recovered carbon fiber material is higher.
本发明的另一目的在于其提供一种用于自无机胶凝材料中回收高性能碳纤维的组合物。Another object of the present invention is to provide a composition for recovering high performance carbon fibers from an inorganic cementitious material.
本发明的其它优势和特点通过下述的详细说明得以充分体现并可通过所附权利要求中特地指出的手段和装置的组合得以实现。Other advantages and features of the invention will be apparent from the description and appended claims appended claims
依本发明,能够实现前述目的和其他目的和优势的本发明自无机胶凝材料中回收高性能碳纤维的方法包括下述步骤:According to the present invention, a method for recovering high performance carbon fibers from an inorganic cementitious material capable of achieving the foregoing and other objects and advantages includes the following steps:
(A)于25℃~75℃的反应温度将碳纤维增强无机(水泥基)复合材料置于电解液中,其中该电解液含有重量比为0.5%~3%的NaCl和1.0g/L~5g/L的催化剂;(A) placing a carbon fiber-reinforced inorganic (cement-based) composite material in an electrolyte at a reaction temperature of 25 ° C to 75 ° C, wherein the electrolyte contains 0.5% to 3% by weight of NaCl and 1.0 g/L to 5 g. /L catalyst;
(B)对放置在电解液中的碳纤维增强水泥基复合材料通电,其中该碳纤维增强水泥 基复合材料与电源的正极相连,控制电流密度为3333.3~6666.7mA/m 2,其中所述电流密度的大小根据所述碳纤维增强无机(水泥基)复合材料中碳纤维材料浸泡于所述电解液内的表面积大小进行计算;和 (B) energizing the carbon fiber reinforced cement-based composite material placed in the electrolyte, wherein the carbon fiber reinforced cement-based composite material is connected to the positive electrode of the power source, and the current density is controlled to be 3333.3 to 6666.7 mA/m 2 , wherein the current density is The size is calculated according to the surface area of the carbon fiber reinforced inorganic (cement-based) composite material in which the carbon fiber material is immersed in the electrolyte; and
(C)通电反应0.5-200小时后,自该电解液中取出生成的碳纤维回收物。(C) After the energization reaction was carried out for 0.5 to 200 hours, the produced carbon fiber recovered product was taken out from the electrolytic solution.
在一实施例中,其中在步骤(C)之后进一步包括步骤:In an embodiment, wherein the step (C) further comprises the step of:
(D)冲洗自该电解液中取出的碳纤维回收物,以清除无机(水泥基)凝胶材料。(D) Flushing the carbon fiber reclaimed material taken out from the electrolyte to remove the inorganic (cement-based) gel material.
在一实施例中,其中根据步骤(D),所述碳纤维回收物表面被设置有间隔分布的孔洞。In an embodiment, wherein the carbon fiber recyclate surface is provided with spaced apart pores according to step (D).
在一实施例中,其中根据步骤(D),各所述孔洞之间的间隔大于0.1mm,冲洗水压高于0.1MPa,冲洗时间不少于3秒。In an embodiment, wherein according to step (D), the interval between each of the holes is greater than 0.1 mm, the flushing water pressure is higher than 0.1 MPa, and the rinsing time is not less than 3 seconds.
依本发明较佳实施例,本发明进一步提供一种用于自无机胶凝材料中回收高性能碳纤维的电解液,其含有:According to a preferred embodiment of the present invention, the present invention further provides an electrolyte for recovering high performance carbon fibers from an inorganic cementitious material, comprising:
0.5%~3%的NaCl;0.5% to 3% NaCl;
1.0g/L~5g/L的HNO 3;和 1.0 g/L to 5 g/L of HNO 3 ; and
80%~98%的水。80% to 98% water.
通过对随后的描述和附图的理解,本发明进一步的目的和优势将得以充分体现。Further objects and advantages of the present invention will be fully realized from the understanding of the appended claims.
本发明的这些和其它目的、特点和优势,通过下述的详细说明,附图和权利要求得以充分体现。These and other objects, features and advantages of the present invention will become apparent from
附图说明DRAWINGS
图1A显示的是碳纤维电化学回收系统的结构示意图。Figure 1A shows a schematic structural view of a carbon fiber electrochemical recovery system.
图1B和图1C显示的是碳纤维增强水泥基复合材料试件的结构示意图。1B and 1C are schematic views showing the structure of a carbon fiber reinforced cement-based composite test piece.
图2显示的是自碳纤维增强水泥基复合材料回收得到的碳纤维回收物。Figure 2 shows a carbon fiber recyclate recovered from a carbon fiber reinforced cementitious composite.
图3A显示的是未经电化学回收处理的碳纤维增强水泥基材料的水泥基与碳纤维相接的界面。Figure 3A shows the interface between the cementitious and carbon fibers of a carbon fiber reinforced cementitious material that has not been electrochemically recycled.
图3B显示的是图3A中方框处部位的细节放大。Figure 3B shows a detail enlargement of the portion of the block in Figure 3A.
图3C显示的是碳纤维回收物的水泥基材料和碳纤维相接的界面。Figure 3C shows the interface between the cementitious material of the carbon fiber recyclate and the carbon fiber.
图3D显示的是图3C中方框处部位的细节放大。Figure 3D shows a detail enlargement of the portion of the block in Figure 3C.
图4显示的是不同分组碳纤维增强水泥基复合材料样本回收得到的碳纤维的量。Figure 4 shows the amount of carbon fiber recovered from samples of different grouped carbon fiber reinforced cementitious composites.
图5显示的是反应过程中,不同分组碳纤维增强水泥基复合材料样本的电压。Figure 5 shows the voltages of different groups of carbon fiber reinforced cementitious composite samples during the reaction.
图6显示的是不同分组碳纤维增强水泥基复合材料样本的回收得到的碳纤维单丝拉伸强度。Figure 6 shows the tensile strength of carbon fiber monofilaments recovered from different groups of carbon fiber reinforced cementitious composite samples.
图7显示的是不同分组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的界面剪切强度。Figure 7 shows the interfacial shear strength of recycled carbon fibers from different grouped carbon fiber reinforced cementitious composite samples.
图8A显示的是碳纤维原丝的表面破坏模式。Figure 8A shows the surface failure mode of the carbon fiber precursor.
图8B显示的是I20S 2.0H 1组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的表面破坏模式。 Figure 8B shows the surface failure mode of the carbon fiber recovered from the I20S 2.0 H 1 carbon fiber reinforced cementitious composite sample.
图8C显示的是I40S 2.0H 1组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的表面破坏模式。 Figure 8C shows the surface failure mode of the carbon fiber recovered from the I40S 2.0 H 1 carbon fiber reinforced cementitious composite sample.
图8D显示的是I20S 2.0H 3组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的表面破坏模式。 Figure 8D shows the surface failure mode of the carbon fiber recovered from the I20S 2.0 H 3 carbon fiber reinforced cementitious composite sample.
图8E显示的是I40S 2.0H 3组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的表面破坏模式。 Figure 8E shows the surface failure mode of the carbon fiber recovered from the I40S 2.0 H 3 carbon fiber reinforced cementitious composite sample.
图8F显示的是I20S 2.0H 5组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的表面破坏模式。 Figure 8F shows the surface failure mode of the carbon fiber recovered from the I20S 2.0 H 5 carbon fiber reinforced cementitious composite sample.
图8G显示的是I40S 2.0H 5组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的表面破坏模式。 Figure 8G shows the surface failure mode of the carbon fiber recovered from the I40S 2.0 H 5 carbon fiber reinforced cementitious composite sample.
图9A显示的是碳纤维原丝表面的SEM扫描图像。Figure 9A shows an SEM scan image of the surface of a carbon fiber precursor.
图9B显示的是I20S 2.0H 1组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的SEM扫描图像。 Figure 9B shows an SEM scan of the carbon fiber recovered from the I20S 2.0 H 1 carbon fiber reinforced cementitious composite sample.
图9C显示的是I40S 2.0H 1组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的SEM扫描图像。 Figure 9C shows an SEM scan of carbon fiber recovered from a sample of I40S 2.0 H 1 carbon fiber reinforced cementitious composite.
图9D显示的是I20S 2.0H 3组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的SEM扫描图像。 Figure 9D shows an SEM scan of the carbon fiber recovered from the I20S 2.0 H 3 carbon fiber reinforced cementitious composite sample.
图9E显示的是I40S 2.0H 3组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的表SEM扫描图像。 Figure 9E shows a SEM scan of the carbon fiber recovered from the I40S 2.0 H 3 carbon fiber reinforced cementitious composite sample.
图9F显示的是I20S 2.0H 5组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的SEM扫描图像。 Figure 9F shows an SEM scan of the carbon fiber recovered from the I20S 2.0 H 5 carbon fiber reinforced cementitious composite sample.
图9G显示的是I40S 2.0H 5组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的SEM扫描图像。 Figure 9G shows an SEM scan of the carbon fiber recovered from the I40S 2.0 H 5 carbon fiber reinforced cementitious composite sample.
图10A和图10B显示的是碳纤维原丝表面的AFM扫描图像。Figures 10A and 10B show AFM scan images of the surface of a carbon fiber precursor.
图10C和图10D显示的是I20S 2.0H 1组碳纤维增强水泥基复合材料样本的回收得到的 碳纤维的AFM扫描图像。 Figures 10C and 10D show AFM scan images of recovered carbon fibers from a sample of I20S 2.0 H 1 carbon fiber reinforced cementitious composites.
图10E和图10F显示的是I40S 2.0H 1组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的AFM扫描图像。 10E and 10F show AFM scan images of recovered carbon fibers of a sample of I40S 2.0 H 1 carbon fiber reinforced cementitious composite.
图10G和图10H显示的是I20S 2.0H 3组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的AFM扫描图像。 Figures 10G and 10H show AFM scan images of recycled carbon fibers from a sample of I20S 2.0 H 3 carbon fiber reinforced cementitious composites.
图10I和图10J显示的是I40S 2.0H 3组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的表AFM扫描图像。 10I and 10J show a table AFM scan image of the recovered carbon fiber of the I40S 2.0 H 3 carbon fiber reinforced cementitious composite sample.
图10K和图10L显示的是I20S 2.0H 5组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的AFM扫描图像。 Figures 10K and 10L show AFM scan images of carbon fibers recovered from samples of the I20S 2.0 H 5 carbon fiber reinforced cementitious composite.
图10M和图10N显示的是I40S 2.0H 5组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的AFM扫描图像。 Figure 10M and Figure 10N show AFM scan images of recycled carbon fibers from a sample of I40S 2.0 H 5 carbon fiber reinforced cementitious composites.
图11A显示的是碳纤维原丝表面的XPS(X射线光电子能谱扫描)扫描全谱图像。Figure 11A shows an XPS (X-ray photoelectron spectroscopy) full spectrum image of the surface of a carbon fiber precursor.
图11B显示的是碳纤维原丝表面的XPS扫描C1s高分辨率窄谱图像。Figure 11B shows an XPS scan C1s high resolution narrow spectrum image of the surface of a carbon fiber precursor.
图11C显示的是I20S 2.0H 1组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的XPS扫描全谱图像。 Figure 11C shows an XPS-scan full-spectrum image of carbon fiber recovered from a sample of I20S 2.0 H 1 carbon fiber reinforced cementitious composite.
图11D显示的是I20S 2.0H 1组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的XPS扫描C1s高分辨率窄谱图像。 Figure 11D shows an XPS scan C1s high resolution narrow-spectrum image of carbon fiber recovered from a sample of I20S 2.0 H 1 carbon fiber reinforced cementitious composite.
图11E显示的是I20S 2.0H 3组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的XPS扫描全谱图像。 Figure 11E shows an XPS-scan full-spectrum image of carbon fiber recovered from a sample of I20S 2.0 H 3 carbon fiber reinforced cementitious composites.
图11F显示的是I20S 2.0H 3组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的XPS扫描C1s高分辨率窄谱图像。 Figure 11F shows a high resolution narrow-spectrum image of XPS scan C1s of carbon fiber recovered from a sample of I20S 2.0 H 3 carbon fiber reinforced cementitious composite.
图11G显示的是I20S 2.0H 5组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的XPS扫描全谱图像。 Figure 11G shows an XPS-scan full-spectrum image of the carbon fiber recovered from the I20S 2.0 H 5 carbon fiber reinforced cementitious composite sample.
图11H显示的是I20S 2.0H 5组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的XPS扫描C1s高分辨率窄谱图像。 Figure 11H shows a high-resolution narrow-spectrum image of XPS scan C1s of carbon fiber recovered from I20S 2.0 H 5 carbon fiber reinforced cementitious composite samples.
图12显示的是不同温度条件下,碳纤维增强水泥基复合材料样本的回收得到的碳纤维的量。Figure 12 shows the amount of carbon fiber recovered from carbon fiber reinforced cementitious composite samples at different temperatures.
图13显示的是不同温度条件下,反应过程中,碳纤维增强水泥基复合材料样本的电压。Figure 13 shows the voltage of a carbon fiber reinforced cementitious composite sample during the reaction at different temperatures.
图14显示的是不同温度条件下,自碳纤维增强水泥基复合材料样本的回收得到的碳 纤维的单丝拉伸强度。Figure 14 shows the tensile strength of monofilaments of carbon fibers recovered from carbon fiber reinforced cementitious composite samples at different temperatures.
图15显示的是不同温度条件下,自碳纤维增强水泥基复合材料样本的回收得到的碳纤维的界面剪切强度。Figure 15 shows the interfacial shear strength of carbon fibers recovered from carbon fiber reinforced cementitious composite samples at different temperatures.
图16A显示的是I20S 2.0H 3T 1组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的表面破坏模式。 Figure 16A shows the surface failure mode of carbon fiber recovered from a sample of I20S 2.0 H 3 T 1 carbon fiber reinforced cementitious composite.
图16B显示的是I40S 2.0H 1组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的表面破坏模式。 Figure 16B shows the surface failure mode of the carbon fiber recovered from the I40S 2.0 H 1 carbon fiber reinforced cementitious composite sample.
图16C显示的是I20S 2.0H 3T 2组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的表面破坏模式。 Figure 16C shows the surface failure mode of the carbon fiber recovered from the I20S 2.0 H 3 T 2 carbon fiber reinforced cementitious composite sample.
图16D显示的是I40S 2.0H 3T 2组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的表面破坏模式。 Figure 16D shows the surface failure mode of the carbon fiber recovered from the I40S 2.0 H 3 T 2 carbon fiber reinforced cementitious composite sample.
图16E显示的是I20S 2.0H 3T 3组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的表面破坏模式。 Figure 16E shows the surface failure mode of the carbon fiber recovered from the I20S 2.0 H 3 T 3 carbon fiber reinforced cementitious composite sample.
图16F显示的是I40S 2.0H 3T 3组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的表面破坏模式。 Figure 16F shows the surface failure mode of the carbon fiber recovered from the I40S 2.0 H 3 T 3 carbon fiber reinforced cementitious composite sample.
图17A显示的是I20S 2.0H 3T 1组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的SEM扫描图像。 Figure 17A shows an SEM scan of the carbon fiber recovered from the I20S 2.0 H 3 T 1 carbon fiber reinforced cementitious composite sample.
图17B显示的是I40S 2.0H 3T 1组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的SEM扫描图像。 Figure 17B shows an SEM scan of the carbon fiber recovered from the I40S 2.0 H 3 T 1 carbon fiber reinforced cementitious composite sample.
图17C显示的是I20S 2.0H 3T 2组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的SEM扫描图像。 Figure 17C shows an SEM scan of the carbon fiber recovered from the I20S 2.0 H 3 T 2 carbon fiber reinforced cementitious composite sample.
图17D显示的是I40S 2.0H 3T 2组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的SEM扫描图像。 Figure 17D shows an SEM scan of the carbon fiber recovered from the I40S 2.0 H 3 T 2 carbon fiber reinforced cementitious composite sample.
图17E显示的是I20S 2.0H 3T 3组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的表SEM扫描图像。 Figure 17E shows a SEM scan of the carbon fiber recovered from the I20S 2.0 H 3 T 3 carbon fiber reinforced cementitious composite sample.
图17F显示的是I40S 2.0H 3T 3组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的SEM扫描图像。 Figure 17F shows an SEM scan of the carbon fiber recovered from the I40S 2.0 H 3 T 3 carbon fiber reinforced cementitious composite sample.
图18A显示的是I20S 2.0组碳纤维增强水泥基复合材料样本于不同温度梯度下回收得到的碳纤维的XRD扫描图谱。 Figure 18A shows an XRD scan of carbon fibers recovered from I20S 2.0 carbon fiber reinforced cementitious composite samples at different temperature gradients.
图18B显示的是I40S 2.0组碳纤维增强水泥基复合材料样本于不同温度梯度下回收得 到的碳纤维的XRD扫描图谱。 Figure 18B shows an XRD scan of carbon fibers recovered from I40S 2.0 carbon fiber reinforced cementitious composite samples at different temperature gradients.
图19A显示的是I20S 2.0H 3T 1组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的XPS扫描全谱图像。 Figure 19A shows an XPS-scan full-spectrum image of carbon fiber recovered from a sample of the I20S 2.0 H 3 T 1 carbon fiber reinforced cementitious composite.
图19B显示的是I20S 2.0H 3T 1组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的XPS扫描C1s高分辨率窄谱图像。 Figure 19B shows a high resolution narrow-spectrum image of XPS scan C1s of carbon fiber recovered from a sample of I20S 2.0 H 3 T 1 carbon fiber reinforced cementitious composite.
图19C显示的是I20S 2.0H 3T 2组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的XPS扫描全谱图像。 Figure 19C shows an XPS-scan full-spectrum image of the carbon fiber recovered from the I20S 2.0 H 3 T 2 carbon fiber reinforced cementitious composite sample.
图19D显示的是I20S 2.0H 3T 2组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的XPS扫描C1s高分辨率窄谱图像。 Figure 19D shows an XPS scan C1s high resolution narrow-spectrum image of carbon fiber recovered from a sample of I20S 2.0 H 3 T 2 carbon fiber reinforced cementitious composite.
图19E显示的是I20S 2.0H 3T 3组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的XPS扫描全谱图像。 Figure 19E shows an XPS-scan full-spectrum image of the carbon fiber recovered from the I20S 2.0 H 3 T 3 carbon fiber reinforced cementitious composite sample.
图19F显示的是I20S 2.0H 3T 3组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的XPS扫描C1s高分辨率窄谱图像。 Figure 19F shows an XPS scan C1s high resolution narrow-spectrum image of carbon fiber recovered from a sample of I20S 2.0 H 3 T 3 carbon fiber reinforced cementitious composite.
图20A显示的是I20S 2.0组碳纤维增强水泥基复合材料样本于不同催化剂浓度下回收得到的碳纤维的XRD扫描图谱。 Figure 20A shows an XRD scan of carbon fibers recovered from I20S 2.0 carbon fiber reinforced cementitious composite samples at various catalyst concentrations.
图20B显示的是I40S 2.0组碳纤维增强水泥基复合材料样本于不同催化剂浓度下回收得到的碳纤维的XRD扫描图谱。 Figure 20B shows an XRD scan of carbon fibers recovered from I40S 2.0 carbon fiber reinforced cementitious composite samples at various catalyst concentrations.
具体实施方式Detailed ways
下述描述被揭露以使本领域技术人员可制造和使用本发明。下述描述中提供的较佳实施例仅作为对本领域技术人员显而易见的示例和修改,其并不构成对本发明范围的限制。下述描述中所定义的一般原理可不背离本发明精神和发明范围地应用于其它实施例、可选替代、修改、等同实施和应用。The following description is disclosed to enable any person skilled in the art to make and use the invention. The preferred embodiments provided in the following description are merely exemplary and modifications that are obvious to those skilled in the art, and are not intended to limit the scope of the invention. The general principles defined in the following description may be applied to other embodiments, alternatives, modifications, equivalents and applications without departing from the spirit and scope of the invention.
参考说明书附图之图1A至图20B,依本发明较佳实施例的用于自无机胶凝材料中回收高性能碳纤维的方法被详细说明,示例性的,采用碳纤维增强水泥基材料解释具体实施方式,其中所述自碳纤维增强水泥基复合材料(废弃物)中回收碳纤维的方法包括下述步骤:Referring to Figures 1A to 20B of the accompanying drawings, a method for recovering high performance carbon fibers from an inorganic cementitious material in accordance with a preferred embodiment of the present invention is described in detail, and an exemplary embodiment is explained using a carbon fiber reinforced cementitious material. The method wherein the method for recovering carbon fibers from a carbon fiber reinforced cement-based composite material (waste) comprises the steps of:
(A)于25℃~75℃的反应温度将碳纤维增强水泥基复合材料放置在电解液中,其中该电解液含有重量比为0.5%~3%的NaCl和1.0g/L~5g/L的催化剂;(A) placing a carbon fiber reinforced cement-based composite material in an electrolyte at a reaction temperature of 25 ° C to 75 ° C, wherein the electrolyte contains 0.5% to 3% by weight of NaCl and 1.0 g/L to 5 g/L. catalyst;
(B)对放置在电解液中的碳纤维增强水泥基复合材料通电,其中该碳纤维增强水泥基复合材料与电源的正极相连,控制电流密度为3333.3~6666.7mA/m 2,其中所述电流密 度的大小根据所述碳纤维增强无机(水泥基)复合材料中碳纤维材料浸泡于所述电解液内的表面积大小进行计算;和 (B) energizing the carbon fiber reinforced cement-based composite material placed in the electrolyte, wherein the carbon fiber reinforced cement-based composite material is connected to the positive electrode of the power source, and the current density is controlled to be 3333.3 to 6666.7 mA/m 2 , wherein the current density is The size is calculated according to the surface area of the carbon fiber reinforced inorganic (cement-based) composite material in which the carbon fiber material is immersed in the electrolyte; and
(C)通电反应0.5-200小时后,自该电解液中取出生成的碳纤维回收物。(C) After the energization reaction was carried out for 0.5 to 200 hours, the produced carbon fiber recovered product was taken out from the electrolytic solution.
值得一提的是,在本发明的所述自无机胶凝材料中回收高性能碳纤维的方法的一些实施例中,所述自无机胶凝材料中回收高性能碳纤维的方法于该步骤(C)之后进一步包括步骤:It is worth mentioning that in some embodiments of the method for recovering high-performance carbon fibers from the inorganic cementitious material of the present invention, the method for recovering high-performance carbon fibers from the inorganic cementing material is in the step (C). Then further steps are included:
(D)冲洗自该电解液中取出的碳纤维回收物,以清除水泥基凝胶。(D) Flushing the carbon fiber reclaimed material taken from the electrolyte to remove the cement-based gel.
进一步的,在该步骤(D)中,其中所述碳纤维回收物表面被设置有间隔分布的孔洞,特别地,各所述孔洞之间的间隔大于0.1mm,冲洗水压高于0.1MPa,冲洗时间不少于3秒。在本文中,电解液指的是含有NaCl、水和催化剂,其被用于自碳纤维增强水泥基复合材料回收碳纤维。示例性地,NaCl浓度分别以重量百分比计量,例如NaCl浓度可为x1(0.5%)、x2(1%)、x3(2%)和x4(3%)。电流(I)大小的衡量尺度为mA,如20mA、40mA。在示例中,当忽略CFRP的厚度时,CFRP试件暴露于电解液中的实验表面积(A)为2×100mm×30mm=6000mm 2,因此对应的电流密度(i=I/A)分别为3333.3、6666.7mA/m 2。具体的碳纤维增强水泥基复合材料的分组及实验参数见表5.1,其中碳纤维增强水泥基复合材料试件的编号由作用电流强度、NaCl浓度、HNO 3浓度和温度共同确定,比如试件编号“I20S 2.0H 3T 40”,第一部分“I20”是指试件施加的恒定电流强度是20mA,第二部分“S 2.0”是指电解液中浓度NaCl为去离子水质量的2%,第三部分“H 3”是指每升电解液中添加的HNO 3浓度为3g/L。第四部分“T 40”是指实验过程中电解液的温度保持在40℃。无第四部分时表明试验在室温中进行(温度为25度) Further, in the step (D), wherein the surface of the carbon fiber recyclate is provided with spaced-apart holes, in particular, the interval between each of the holes is greater than 0.1 mm, the flushing water pressure is higher than 0.1 MPa, and the flushing is performed. The time is no less than 3 seconds. As used herein, electrolyte refers to the inclusion of NaCl, water, and a catalyst that is used to recover carbon fibers from a carbon fiber reinforced cementitious composite. Illustratively, the NaCl concentration is measured in weight percent, for example, the NaCl concentration may be x1 (0.5%), x2 (1%), x3 (2%), and x4 (3%). The current (I) size is measured in mA, such as 20 mA, 40 mA. In the example, when the thickness of the CFRP is ignored, the experimental surface area (A) of the CFRP test piece exposed to the electrolyte is 2 × 100 mm × 30 mm = 6000 mm 2 , so the corresponding current density (i = I / A) is 3333.3, respectively. , 6666.7 mA / m 2 . The grouping and experimental parameters of specific carbon fiber reinforced cement-based composites are shown in Table 5.1. The number of carbon fiber reinforced cement-based composite specimens is determined by the applied current intensity, NaCl concentration, HNO 3 concentration and temperature, such as the test piece number “I20S”. 2.0 H 3 T 40 ”, the first part “I20” means that the constant current intensity applied by the test piece is 20 mA, and the second part “S 2.0 ” means that the concentration of NaCl in the electrolyte is 2% of the mass of deionized water, the third part "H 3 " means that the concentration of HNO 3 added per liter of the electrolyte is 3 g/L. The fourth part "T 40 " means that the temperature of the electrolyte is maintained at 40 ° C during the experiment. Without the fourth part, the test is carried out at room temperature (temperature is 25 degrees)
如说明书附图之图1A所示,自CFRP增强水泥基复合材料回收碳纤维的(电化学)回收系统包括直流电源,为系统提供单向工作电流;阴阳极材料,其中待回收的碳纤维增强水泥基复合材料板(回收样本)作为阳极与电源正极相连,不锈钢片作为阴极与电源负极相连;电解液,含有NaCl、水(溶剂)和催化剂;数据记录仪(Datalog),与回收样本及不锈钢片并联,监测样本电压变化。示例性地,碳纤维增强水泥基复合材料板与不锈钢片平行放置,且两者距离固定为50mm。As shown in Figure 1A of the accompanying drawings, the (electrochemical) recovery system for recovering carbon fibers from CFRP reinforced cement-based composite materials includes a DC power source to provide a unidirectional operating current for the system; a cathode-anode material in which the carbon fiber reinforced cement base to be recovered The composite plate (recycled sample) is connected as an anode to the positive electrode of the power supply, the stainless steel piece is connected as a cathode to the negative electrode of the power source; the electrolyte contains NaCl, water (solvent) and a catalyst; the data log (Datalog) is connected in parallel with the recovered sample and the stainless steel piece. , monitor sample voltage changes. Illustratively, the carbon fiber reinforced cementitious composite panel is placed in parallel with the stainless steel sheet and the distance between the two is fixed at 50 mm.
如说明书附图之图2所示,经点化学处理,自碳纤维增强水泥基复合材料回收得到的碳纤维回收物,质地较软。As shown in Figure 2 of the accompanying drawings, the carbon fiber recovered material recovered from the carbon fiber reinforced cement-based composite material is soft in texture by point chemical treatment.
如说明书附图之图3A和图3B所示,未经电化学回收处理的碳纤维增强水泥基材料的水泥基与碳纤维相接的界面,其棱状沟槽结构完整和规则,能够与碳纤维形成强大的机械咬合作用,界面只有极小的孔洞,看不到裂缝裂纹等缺陷。As shown in FIG. 3A and FIG. 3B of the drawings of the specification, the interface between the cement-based and carbon fibers of the carbon fiber reinforced cement-based material which is not electrochemically treated has a rib-shaped groove structure which is complete and regular and can form a strong bond with carbon fibers. The mechanical bite is used, the interface has only very small holes, and no cracks and other defects are visible.
如说明书附图之图3C和图3D所示,碳纤维回收物的水泥基材料和碳纤维相接的界面的规则菱形沟槽结构已经被纵横向的大裂缝所斩断分割成破碎的小单元,呈蓬松状,同时还有很多较大的裂纹孔洞分布其中,孔隙率剧烈增大,界面已经完全丧失了与碳纤维的机械咬合作用,粘结力大幅度下降。As shown in FIG. 3C and FIG. 3D of the drawings of the specification, the regular rhombic groove structure of the interface between the cement-based material of the carbon fiber recyclate and the carbon fiber interface has been divided into broken small units by large cracks in the longitudinal and lateral directions. Fluffy, and there are many large crack holes in which the porosity increases sharply, the interface has completely lost the mechanical bite with carbon fiber, and the adhesion is greatly reduced.
如说明书附图之图4所示,不同分组碳纤维增强水泥基复合材料样本回收得到的碳纤维的量有所不同,碳纤维回收量随HNO 3浓度增大呈现先增后降趋势,HNO 3浓度为3g/L时,碳纤维回收量最大。在HNO 3浓度为1g/L分组中,碳纤维回收量明显降低。 As shown in Figure 4 of the accompanying drawings, the amount of carbon fiber recovered from different carbon fiber reinforced cement-based composite samples is different. The carbon fiber recovery increases first and then decreases with the increase of HNO 3 concentration, and the concentration of HNO 3 is 3g. At /L, the amount of carbon fiber recovered is the largest. In the HNO 3 concentration of 1 g/L group, the amount of carbon fiber recovered was significantly reduced.
如说明书附图之图5所示,反应过程中,不同分组碳纤维增强水泥基复合材料样本的电压变化。其中H 0组样本的电压最高,相对波动最大;H 5组样本的电压低于H 0组,但仍然比较高;H 3与H 1组样本电压较低。在总体上,I40系列样本电压比I20系列大,S 3.0系列样本电压比S 2.0系列大。 As shown in Figure 5 of the accompanying drawings, the voltage variation of different groups of carbon fiber reinforced cementitious composite samples during the reaction. Among them, the H 0 group has the highest voltage and the highest relative fluctuation; the H 5 group has lower voltage than the H 0 group, but it is still relatively high; the H 3 and H 1 groups have lower sample voltages. In general, the I40 series sample voltage is larger than the I20 series, and the S 3.0 series sample voltage is larger than the S 2.0 series.
如说明书附图之图6所示,不同分组碳纤维增强水泥基复合材料样本的回收得到的碳纤维单丝拉伸强度,其中回收得到的碳纤维的单丝拉伸强度随HNO 3浓度增大而呈下降趋势,在0~3(g/L)的HNO 3浓度区间,碳纤维的拉伸强度下降幅度较小,3~5(g/L)的HNO 3浓度区间,回收得到的碳纤维拉伸强度急剧下降。 As shown in Figure 6 of the accompanying drawings, the tensile strength of carbon fiber monofilament recovered from different carbon fiber reinforced cementitious composite samples, wherein the tensile strength of the recovered carbon fiber decreases with increasing HNO 3 concentration. In the trend of 0 to 3 (g/L) HNO 3 concentration range, the tensile strength of carbon fiber decreases slightly, and the tensile strength of carbon fiber recovered is sharply decreased in the range of HNO 3 concentration of 3 to 5 (g/L). .
如说明书附图之图7所示,不同分组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的界面剪切强度,其中回收得到的碳纤维的界面剪切强度随HNO 3浓度增大而下降,但是H 1和H 3组回收得到的碳纤维比原丝剪切强度大。 As shown in Figure 7 of the accompanying drawings, the interfacial shear strength of carbon fibers recovered from different carbon fiber reinforced cementitious composite samples is reduced, and the interfacial shear strength of the recovered carbon fibers decreases with increasing HNO 3 concentration, but The carbon fibers recovered from the H 1 and H 3 groups have greater shear strength than the original fibers.
如说明书附图之图8A所示,碳纤维原丝的表面破坏模式为DB。As shown in Fig. 8A of the drawings of the specification, the surface failure mode of the carbon fiber precursor is DB.
如说明书附图之图8B所示,I20S 2.0H 1组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的表面破坏模式为DB。 As shown in Fig. 8B of the accompanying drawings, the surface damage mode of the carbon fiber recovered from the I20S 2.0 H 1 carbon fiber reinforced cement-based composite sample is DB.
如说明书附图之图8C所示,I40S 2.0H 1组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的表面破坏模式为DB。 As shown in Figure 8C of the accompanying drawings, the surface failure mode of the carbon fiber recovered from the I40S 2.0 H 1 carbon fiber reinforced cementitious composite sample is DB.
如说明书附图之图8D所示,I20S 2.0H 3组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的表面破坏模式为CB。 As shown in Fig. 8D of the accompanying drawings, the surface failure mode of the carbon fiber recovered from the I20S 2.0 H 3 carbon fiber reinforced cement-based composite sample is CB.
如说明书附图之图8E所示,I40S 2.0H 3组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的表面破坏模式为CB。 As shown in Fig. 8E of the accompanying drawings, the surface failure mode of the carbon fiber recovered from the I40S 2.0 H 3 carbon fiber reinforced cement-based composite sample is CB.
如说明书附图之图8F所示,I20S 2.0H 5组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的表面破坏模式为CB。 As shown in Fig. 8F of the drawings, the surface damage mode of the carbon fiber recovered from the I20S 2.0 H 5 carbon fiber reinforced cementitious composite sample is CB.
如说明书附图之图8G所示,I40S 2.0H 5组碳纤维增强水泥基复合材料样本的回收得到 的碳纤维的表面破坏模式为EB。 As shown in Figure 8G of the accompanying drawings, the surface failure mode of the carbon fiber recovered from the I40S 2.0 H 5 carbon fiber reinforced cement-based composite sample is EB.
如说明书附图之图9A所示,碳纤维原丝表面的SEM扫描图像显示其表面光滑。As shown in Figure 9A of the accompanying drawings, the SEM scan image of the surface of the carbon fiber precursor shows that the surface is smooth.
如说明书附图之图9B和图9C所示,I20S 2.0H 1组和I40S 2.0H 1组碳纤维增强水泥基复合材料样本的回收得到的碳纤维表面除了附着有极少量的水泥凝胶外,并未看到裂纹裂缝凹坑等缺陷,十分完整。 As shown in Figure 9B and Figure 9C of the accompanying drawings, the carbon fiber surface of the I20S 2.0 H 1 group and the I40S 2.0 H 1 carbon fiber reinforced cement matrix composite sample was recovered except that a very small amount of cement gel was attached. Seeing defects such as crack cracks and pits is very complete.
如说明书附图之图9D和图9E所示,I20S 2.0H 3组和I40S 2.0H 3组碳纤维增强水泥基复合材料样本的回收得到的碳纤维表面很干净,极少水泥凝胶颗粒残留,但是在个别根数的碳纤维表面发现有横向裂纹,在裂纹处形成薄弱层,造成碳纤维拉伸强度下降。 As shown in Figure 9D and Figure 9E of the accompanying drawings, the carbon fiber surface of the I20S 2.0 H 3 group and the I40S 2.0 H 3 carbon fiber reinforced cement matrix composite sample is clean, and few cement gel particles remain, but A cross-crack is found on the surface of the carbon fiber of individual numbers, and a weak layer is formed at the crack, resulting in a decrease in the tensile strength of the carbon fiber.
如说明书附图之图9F和图9G所示,I20S 2.0H 5组和I40S 2.0H 5组碳纤维增强水泥基复合材料样本的回收得到的碳纤维表面的水泥凝胶颗粒较多,在碳纤维表面发现有纵向裂缝和横向裂纹,且深度不浅,减小了碳纤维的受力截面,因此H 5系列回收得到的碳纤维的拉伸强度严重下降。 As shown in Figure 9F and Figure 9G of the drawings, the carbon fiber surface of the I20S 2.0 H 5 group and the I40S 2.0 H 5 carbon fiber reinforced cement matrix composite sample is recovered, and many cement gel particles are found on the surface of the carbon fiber. Longitudinal cracks and transverse cracks, and the depth is not shallow, reducing the force cross section of the carbon fiber, so the tensile strength of the carbon fiber recovered by the H 5 series is seriously degraded.
如说明书附图之图10A至图10N所示,各个分组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的AFM扫描图像表明,当HNO 3浓度较低时,电化学回收过程的小量氧化刻蚀会增大碳纤维的界面剪切强度,而HNO 3浓度增大到一定程度时,过量的氧化刻蚀反而使碳纤维的界面剪切强度降低。 As shown in Figures 10A to 10N of the accompanying drawings, the AFM scan image of the carbon fiber recovered from each of the grouped carbon fiber reinforced cementitious composite samples shows that when the concentration of HNO 3 is low, a small amount of oxidation of the electrochemical recovery process is shown. The etch will increase the interfacial shear strength of the carbon fiber, and when the HNO 3 concentration is increased to a certain extent, the excessive oxidative etching reduces the interfacial shear strength of the carbon fiber.
如说明书附图之图11A至图11H所示,各个分组碳纤维增强水泥基复合材料样本回收得到的碳纤维的XPS扫描全谱图像和C1s高分辨率窄谱图像表明,碳纤维在回收过程经历了一定程度的氧化,表面含氧量增大,提高了表面活性,并且O~C=O键出现,极大提高了碳纤维与环氧树脂的化学键结合能力;从回收得到的碳纤维的氧碳比和官能团含量来看,HNO 3浓度为1(g/L)时,碳纤维氧化程度过低,当HNO 3浓度为3(g/L)时,碳纤维氧化程度最好,增大HNO 3浓度只是使碳纤维表面C=O键增多。 As shown in Figures 11A to 11H of the accompanying drawings, XPS scanning full-spectrum images and C1s high-resolution narrow-spectrum images of carbon fibers recovered from samples of each group of carbon fiber reinforced cement-based composite materials show that carbon fiber has undergone a certain degree in the recovery process. Oxidation, surface oxygen content increases, surface activity is increased, and O~C=O bond appears, which greatly improves the chemical bonding ability of carbon fiber and epoxy resin; the oxygen-carbon ratio and functional group content of carbon fiber recovered from recovery It can be seen that when the concentration of HNO 3 is 1 (g/L), the degree of oxidation of carbon fiber is too low. When the concentration of HNO 3 is 3 (g/L), the degree of oxidation of carbon fiber is the best. Increasing the concentration of HNO 3 is only to make the surface of carbon fiber C. The =O key increases.
如说明书附图之图12所示,不同温度条件下,碳纤维增强水泥基复合材料样本的回收得到的碳纤维的量随温度的升高呈现先高后低趋势,在温度为40℃时,碳纤维回收量最大。As shown in Figure 12 of the accompanying drawings, the amount of carbon fiber recovered from the carbon fiber reinforced cement-based composite sample at different temperatures shows a high first and then a low temperature, and the carbon fiber is recovered at a temperature of 40 ° C. The largest amount.
如说明书附图之图13所示,不同温度条件下,反应过程中,碳纤维增强水泥基复合材料样本的电压表明,碳纤维增强水泥基复合材料样本的电压较低,不同分组样本的电压差异值很小,表明在高温条件下,样本的系统阻值非常小,且所有样本的电压在电化学回收周期基本保持稳定。As shown in Figure 13 of the accompanying drawings, the voltage of the carbon fiber reinforced cement-based composite sample during the reaction process at different temperature conditions indicates that the voltage of the carbon fiber reinforced cement-based composite sample is low, and the voltage difference values of different grouped samples are very high. Small, indicating that under high temperature conditions, the system resistance of the sample is very small, and the voltage of all samples is basically stable during the electrochemical recovery cycle.
如说明书附图之图14所示,不同温度条件下,自碳纤维增强水泥基复合材料样本的 回收得到的碳纤维的单丝拉伸强度随温度的增加呈现先下降然后一直缓慢上升的趋势。As shown in Figure 14 of the accompanying drawings, the tensile strength of the monofilament of the carbon fiber recovered from the carbon fiber reinforced cementitious composite sample at different temperature conditions first decreases and then increases slowly.
如说明书附图之图15所示,不同温度条件下,自碳纤维增强水泥基复合材料样本的回收得到的碳纤维的界面剪切强度的随温度升高,出现先下降然后增高再下降趋势。As shown in Figure 15 of the accompanying drawings, the interfacial shear strength of carbon fiber recovered from carbon fiber reinforced cement-based composite samples with different temperature conditions increases first and then decreases and then decreases.
如说明书附图之图16A至图16F所示,各个分组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的表面破坏模式,除了I40S 2.0H 3T 2的破坏模式为CB,其他样本的破坏模式均为DB。 As shown in Fig. 16A to Fig. 16F of the accompanying drawings, the surface failure mode of the carbon fiber recovered from the sample of each group of carbon fiber reinforced cement-based composite materials, except that the failure mode of I40S 2.0 H 3 T 2 is CB, the failure mode of other samples Both are DB.
如说明书附图之图17A至图17F所示,各个分组碳纤维增强水泥基复合材料样本的回收得到的碳纤维表面裂纹裂缝等缺陷较少,说明缩短回收周期减少回收过程的氧化和腐蚀等损伤。As shown in FIG. 17A to FIG. 17F of the drawings of the specification, the defects of the surface cracks of the carbon fiber obtained by the recovery of the sample of the carbon fiber reinforced cement-based composite materials are less, indicating that the recovery cycle is shortened to reduce the oxidation and corrosion of the recovery process.
如说明书附图之图19A至图19F所示,各个分组碳纤维增强水泥基复合材料样本的回收得到的碳纤维的XPS扫描全谱图像和XPS扫描C1s高分辨率窄谱图像表明,相比常温状态T 0(25℃),高温状态下碳纤维表面引入的氧更多;在温度为T 1(40℃)时,回收得到的碳纤维表面的氧含量及强亲水性官能团O~C=O含量最多,随着温度的继续上升二者而有所下降;然而碳纤维表面C~Cl键含量高达8.2%,受到较为严重的氯化,造成碳纤维拉伸强度及剪切强度一定程度下降。 As shown in FIG. 19A to FIG. 19F of the drawings of the specification, the XPS-scan full-spectrum image of the carbon fiber recovered from each of the grouped carbon fiber reinforced cementitious composite samples and the high-resolution narrow-spectrum image of the XPS scan C1s show that the temperature is higher than the normal temperature state T. 0 (25 ° C), the oxygen introduced on the surface of the carbon fiber is more at high temperature; at the temperature of T 1 (40 ° C), the oxygen content on the surface of the recovered carbon fiber and the strong hydrophilic functional group O~C=O content are the most. As the temperature continues to rise, there is a decrease; however, the content of C-Cl bond on the surface of carbon fiber is as high as 8.2%, which is subject to more serious chlorination, which causes the tensile strength and shear strength of carbon fiber to decrease to some extent.
进一步地,本文将结合下述具体示例,详细说明本发明。Further, the present invention will be described in detail in conjunction with the following specific examples.
示例1:原材料(碳纤维增强水泥基复合材料)的准备Example 1: Preparation of raw materials (carbon fiber reinforced cement-based composite)
本实验的碳纤维增强水泥基复合材料由CFRP和水泥基胶凝材料两大部分组成。The carbon fiber reinforced cement-based composite material of this experiment consists of two major parts, CFRP and cement-based cementitious materials.
CFRP材料选用南京海拓复合材料公司生产的HITEX-C300型号碳纤维布,为12K单向编织布,密度为300g/m2。水泥选用东莞产地的华润牌PO42.5R极普通复合硅酸盐水泥。硅粉为产自上海的西肯硅粉,高分子聚合物为DY-5025(德国)型号的可再分散粉。选用香港卡本有限公司生产的碳纤维短丝,长度约为3mm。选用西陇化工有限公司生产的氯化钠(分析纯)和HNO 3(分析纯),氯化钠的质量分数为99.5%,B的质量分数为65%—68%。在碳纤维增强水泥基复合材料中,碳纤维布居于中间,水泥基材料的具体成分及含量见表1.1。 The CFRP material is selected from the HITEX-C300 carbon fiber cloth produced by Nanjing Haituo Composite Materials Co., Ltd., which is a 12K unidirectional woven fabric with a density of 300g/m2. The cement is selected from the China Resources brand PO42.5R ordinary composite Portland cement produced in Dongguan. The silicon powder is a Siken silicon powder produced in Shanghai, and the high molecular polymer is a redispersible powder of the DY-5025 (Germany) model. The carbon fiber short yarn produced by Hong Kong Kaben Co., Ltd. is selected to have a length of about 3 mm. Sodium chloride (analytical grade) and HNO 3 (analytical grade) produced by Xiqiao Chemical Co., Ltd. were selected. The mass fraction of sodium chloride was 99.5%, and the mass fraction of B was 65%-68%. In the carbon fiber reinforced cement-based composite material, the carbon fiber cloth is in the middle, and the specific composition and content of the cement-based material are shown in Table 1.1.
碳纤维增强水泥基复合材料试件尺寸为30mm×245mm×4mm。沿碳纤维增强水泥基复合材料厚度方向,上下各为约2毫米厚的水泥基材料,中间是碳纤维布,如图1B和图1C所示。沿其长度方向被分为三个区域,分别为:一区即为试验区(Test region),被用来回收碳纤维的区域,长度为100mm;二区即保护区(Protected region),该区域绝缘防 水,以确保试验区面积在实验过程中的保持大小一致,长度为80mm;三区即接电区(Electrical connection region),用来连接线路不锈钢片接头,保证电路连通性,长度为65mm,为了取得更好的导电性,其中后面20mm为碳纤维布,与不锈钢片连接。因此,上述碳纤维增强水泥基复合材料中碳纤维材料浸泡于上述回收装置中电解液内的表面积大小为100mm×30mm×2=6000mm 2The carbon fiber reinforced cement-based composite test piece has a size of 30 mm × 245 mm × 4 mm. Along the thickness direction of the carbon fiber reinforced cementitious composite material, the cement material is about 2 mm thick on the upper and lower sides, and the carbon fiber cloth is in the middle, as shown in FIG. 1B and FIG. 1C. It is divided into three areas along its length, namely: one area is the test area, the area used to recover carbon fiber, the length is 100mm; the second area is the protected area, which is insulated Waterproof to ensure that the area of the test area is consistent during the experiment, the length is 80mm; the third area is the electrical connection region, which is used to connect the stainless steel joints of the circuit to ensure the circuit connectivity, the length is 65mm, in order to A better electrical conductivity is achieved, in which the rear 20mm is a carbon fiber cloth, which is connected to the stainless steel sheet. Therefore, the surface area of the carbon fiber material in the carbon fiber reinforced cement-based composite material soaked in the electrolyte in the above-mentioned recovery device is 100 mm × 30 mm × 2 = 6000 mm 2 .
复合材料的制作过程尽量接近土木工程领域施工方法,浇筑1天后拆模,然后放进标准养护室养护28天。养护结束后的复合材料放置在实验室条件下7天,自然干燥,然后进行保护区封装。保护区由五层组成,由里及外分别为卡夫特硅橡胶—绝缘胶带—环氧密封胶—绝缘胶带—环氧密封胶。首先在干净干燥的复合材料板试件保护区表面涂刷一层均匀的卡夫特硅橡胶,置于实验室条件下24小时自然晾干;然后在硅橡胶面使用绝缘胶布包裹;接着使用环氧密封胶进行固封,置于实验室条件下48小时自然固化;然后再使用绝缘胶布包裹;最后再使用环氧密封胶进行固封,置于实验室条件下48小时自然固化。The manufacturing process of the composite material is as close as possible to the construction method in the civil engineering field. After pouring for 1 day, the mold is removed and then placed in the standard curing room for 28 days. After the curing, the composite material was placed under laboratory conditions for 7 days, dried naturally, and then packaged in a protected area. The protection zone consists of five layers, which are Kraft Silicone Rubber - Insulation Tape - Epoxy Sealant - Insulation Tape - Epoxy Sealant. Firstly, apply a uniform layer of Kraft silicone rubber on the surface of the clean and dry composite board test piece protection surface, and dry it under laboratory conditions for 24 hours; then wrap it on the silicone rubber surface with insulating tape; then use the ring. The oxygen sealant was solid-sealed and placed in a laboratory condition for 48 hours to be naturally cured; then it was wrapped with an insulating tape; finally, it was sealed with an epoxy sealant and allowed to cure under laboratory conditions for 48 hours.
表1.1碳纤维增强水泥基胶凝材料的具体成分含量Table 1.1 Specific content of carbon fiber reinforced cement-based cementitious materials
Figure PCTCN2018075922-appb-000001
Figure PCTCN2018075922-appb-000001
示例2:回收实验系统与实验参数设计Example 2: Recycling experimental system and experimental parameter design
如附图之图1A所示,碳纤维(实验)回收系统装置主要包括四部分组成:直流电源,为系统提供单向工作电流;阴阳极,回收样本作为阳极与电源正极相连,消耗降解水泥基胶体,不锈钢片作为阴极与电源负极相连;电解液,包括不同浓度的NaCl基础溶液与催化剂HNO 3;数据记录仪(Datalog),与回收样本及不锈钢片并联,监测样本电压变化。回收样本与不锈钢片平行放置并且距离固定为50m。 As shown in Figure 1A of the accompanying drawings, the carbon fiber (experimental) recovery system device mainly comprises four parts: a DC power supply, providing a unidirectional working current for the system; a cathode and anode, the recovered sample is connected as an anode to the positive electrode of the power source, and the degraded cement-based colloid is consumed. The stainless steel piece is connected as a cathode to the negative pole of the power source; the electrolyte includes different concentrations of NaCl base solution and catalyst HNO 3 ; the data log (Datalog) is connected in parallel with the recovered sample and the stainless steel piece to monitor the sample voltage change. The recovered sample was placed in parallel with the stainless steel sheet and the distance was fixed at 50 m.
实验设计主要考虑参数包括电流密度、溶液中的NaCl浓度、催化剂HNO 3浓度以及温度影响等。为了更有效地研究各参数对碳纤维回收效果和效率的影响,本研究设计了两个系列试验。 The experimental design mainly considers parameters including current density, NaCl concentration in solution, catalyst HNO 3 concentration, and temperature effects. In order to study the effects of various parameters on the recovery and efficiency of carbon fiber more effectively, two series of experiments were designed in this study.
在第一系列试验设计中,考虑了:(1)两个电流强度(20mA、40mA),基于示例1中所述碳纤维增强水泥基复合材料中碳纤维材料浸泡于上述回收装置中电解液内的表面积大小为100mm×30mm×2=6000mm 2,可知对应两个电流密度(3333.3mA/m 2、6666.7mA/m 2);(2)两个电解液的氯化钠浓度(2%、3%);(3)四个催化剂硝酸浓度(0g/L、1g/L、3g/L和5g/L)。由此可得16种参数条件,每种试验条件包括3个平行试件,其详细的试件分组和实验参数见表1。 In the first series of experimental designs, (1) two current intensities (20 mA, 40 mA) were considered, based on the surface area of the carbon fiber material immersed in the electrolyte in the above-mentioned recovery device in the carbon fiber reinforced cement-based composite material described in Example 1. The size is 100mm × 30mm × 2 = 6000mm 2 , which means that the two current densities (3333.3mA/m 2 , 6666.7mA/m 2 ); (2) the sodium chloride concentration of the two electrolytes (2%, 3%) (3) Four catalyst nitric acid concentrations (0 g/L, 1 g/L, 3 g/L, and 5 g/L). Thus, 16 kinds of parameter conditions can be obtained. Each test condition includes 3 parallel test pieces. The detailed test piece grouping and experimental parameters are shown in Table 1.
在第二系列试验设计中,首先选取第一系列所得的较优方案,在此基础上考虑温度对碳纤维性能和回收效率的影响。因此,第二系列试验参数包括:(1)两个电流值(20mA、40mA),对应两个电流密度(3333.3mA/m2、6666.7mA/m2);(2)一个电解液的氯化钠浓度(2%);(3)一个催化剂硝酸浓度(3g/L)以及(4)三个温度梯度(40℃、60℃和75℃)。由此可得6种参数条件,每种试验条件包括3个平行试件,其详细的试件分组和实验参数见表2。值得注意的是,为了在常温常压下实现回收,实验设置的最高温度仅为75℃,并没有考虑过高温度条件。In the second series of experimental design, the first series of the best solutions were selected, and the effect of temperature on carbon fiber performance and recovery efficiency was considered. Therefore, the second series of test parameters include: (1) two current values (20 mA, 40 mA), corresponding to two current densities (3333.3 mA / m2, 6666.7 mA / m2); (2) sodium chloride concentration of an electrolyte (2%); (3) one catalyst nitric acid concentration (3 g/L) and (4) three temperature gradients (40 ° C, 60 ° C and 75 ° C). Six parameters can be obtained, each of which includes three parallel test pieces. The detailed test piece grouping and experimental parameters are shown in Table 2. It is worth noting that in order to achieve recovery at normal temperature and pressure, the maximum temperature set by the experiment is only 75 ° C, and the high temperature conditions are not considered.
试件编号由作用电流强度、NaCl浓度、HNO 3浓度和温度共同确定,比如试件编号“I20S 2.0H 3T 40”,第一部分“I20”是指试件施加的恒定电流强度是20mA,第二部分“S2”是指电解液中浓度NaCl为去离子水质量的2%,第三部分“H 3”是指每升电解液中添加的HNO 3浓度为3g/L。第四部分“T40”是指实验过程中电解液的温度保持在40℃。无第四部分时表明试验在室温中进行(温度为25度) The test piece number is determined by the action current intensity, NaCl concentration, HNO 3 concentration and temperature. For example, the test piece number is “I20S 2.0 H 3 T 40 ”. The first part “I20” means that the constant current intensity applied by the test piece is 20 mA. two-part "S2" refers to the concentration of the electrolyte is NaCl in deionized water 2% by mass of the third portion "H 3" refers to the concentration of HNO 3 per liter of the electrolytic solution was added 3g / L. The fourth part "T40" means that the temperature of the electrolyte is kept at 40 °C during the experiment. Without the fourth part, the test is carried out at room temperature (temperature is 25 degrees)
示例3:实验测试方法Example 3: Experimental test method
3.1样本电压监测3.1 sample voltage monitoring
选用日本日置电机株式会社生产的HIOKI-LR8400型号数据记录仪(Datalog),每小时采集1次数据。采频频率为1h/次,电源频率为50HZ。The HIOKI-LR8400 data logger (Datalog) manufactured by Nissin Electric Co., Ltd. was used to collect data once per hour. The frequency of the frequency is 1h/time and the power frequency is 50HZ.
3.2碳纤维单丝拉伸性能测试3.2 Carbon fiber monofilament tensile performance test
依照碳纤维单丝拉伸强度测试规范ISO 11566[54],选用美国安捷伦公司生产的nano UTM 150型号纳米拉伸仪进行碳纤维单丝拉伸实验;测试系统为UTM-Bionix Standard Toecomp Quasistatic。测试参数设定如下:作用荷载750μN,拉伸速率为0.2μm/s,荷载分辨率为50nN,位移分辨率<0.1nm,拉伸分辨率为35nm,作动器最大位移1mm。测试温度为20℃-30℃,空气湿度40%。According to the carbon fiber monofilament tensile strength test specification ISO 11566 [54], the carbon fiber monofilament tensile test was carried out using a nano UTM 150 model nano-stretcher manufactured by Agilent, USA; the test system was UTM-Bionix Standard Toecomp Quasistatic. The test parameters were set as follows: application load 750 μN, tensile rate 0.2 μm/s, load resolution 50 nN, displacement resolution <0.1 nm, tensile resolution 35 nm, actuator maximum displacement 1 mm. The test temperature is 20 ° C - 30 ° C, and the air humidity is 40%.
进行碳纤维单丝拉伸测试前,需将碳纤维单丝固定在尺寸为15mm 20mm的相片纸上,相片纸中间为直径6mm的圆孔,使用膏状胶水将碳纤维单丝粘在圆孔水平方向直径上,纤维不能过紧或过于松弛。Before the carbon fiber monofilament tensile test, the carbon fiber monofilament should be fixed on the photo paper of 15mm 20mm in size, and the middle of the photo paper is a circular hole with a diameter of 6mm. The carbon fiber monofilament is adhered to the horizontal diameter of the round hole by using the paste glue. On the fiber, the fiber should not be too tight or too loose.
样本制作完成后,置于实验室条件一天,待胶水自然晾干。即可将样本装进纳米拉伸仪夹具,然后将相片纸两侧边沿剪断,最后开始进行测试。碳纤维单丝测试长度为61mm,每个样本需测试的样品为20个,碳纤维单丝强度结果为20个样品强度平均值。单丝拉伸强度公式如下:After the sample is prepared, it is placed in laboratory conditions for one day, and the glue is allowed to dry naturally. The sample can be loaded into the nano-tensile fixture, then the edges of the photo paper are cut and the test begins. The carbon fiber monofilament test length is 61 mm, the number of samples to be tested per sample is 20, and the carbon fiber monofilament strength result is 20 sample intensity average. The tensile strength formula of the monofilament is as follows:
Figure PCTCN2018075922-appb-000002
Figure PCTCN2018075922-appb-000002
式中σ f—单丝拉伸强度(MPa) Where σ f — tensile strength of monofilament (MPa)
F f—单丝断裂最大荷载(N) F f — monofilament fracture maximum load (N)
d—单丝直径(mm)D—monofilament diameter (mm)
选用长春产业光电技术有限公司生产的激光测径仪测量碳纤维单丝直径。将样本放置于样品架上,利用衍射原理,测量单丝的衍射暗纹间距,通过公式换算即可计算得到单丝的精确直径,公式如下:The diameter of the carbon fiber monofilament was measured using a laser caliper manufactured by Changchun Industrial Optoelectronic Technology Co., Ltd. The sample is placed on the sample holder, and the diffraction dark line spacing of the monofilament is measured by the diffraction principle. The exact diameter of the monofilament can be calculated by formula conversion, and the formula is as follows:
d=kLλ/x k=Lλ/S   (2-2) d=kLλ/x k =Lλ/S (2-2)
式中d—单丝直径(nm)Where d-monofilament diameter (nm)
S—暗纹直径(cm)S—dark line diameter (cm)
L—样品到衍射屏的距离L—the distance from the sample to the diffraction screen
x k—第k极暗纹到光轴的距离 x k — the distance from the kth to the optical axis
参数设置:L=60cm,λ=532nmParameter setting: L=60cm, λ=532nm
3.3碳纤维单丝界面剪切强度测试3.3 Carbon fiber monofilament interface shear strength test
选用日本东荣株式会社生产的HM410复合材料界面特征评价装置进行微滴包埋测试。测试参数设定如下:测试速度为0.12mm/min,显微镜倍率为2倍。The HM410 composite interface feature evaluation device manufactured by Japan Toyon Co., Ltd. was used for the droplet embedding test. The test parameters were set as follows: the test speed was 0.12 mm/min, and the microscope magnification was 2 times.
根据文献研究 [55],测试树脂球的直径范围宜选定为40μm~80μm。每个样本测试的树脂球为5个,界面剪切强度结果取其平均值。界面剪切强度公式如下: According to literature studies [55] , the diameter of the test resin sphere should be selected from 40 μm to 80 μm. The number of resin balls tested in each sample was 5, and the interfacial shear strength results were averaged. The interface shear strength formula is as follows:
Figure PCTCN2018075922-appb-000003
Figure PCTCN2018075922-appb-000003
式中F—荷载值(μN)Where F - load value (μN)
d—单丝直径(μm)D—monofilament diameter (μm)
l—树脂球直径(μm)L—resin ball diameter (μm)
3.4环境扫描电子显微镜(ESEM)测试3.4 Environmental Scanning Electron Microscopy (ESEM) Test
选用美国FEI公司的Quanta TM 250FEG型号环境扫描电子显微镜,对回收得到的碳纤维表面形貌状况进行观察分析。选择高真空模式,工作距离约为10mm,测试加速电压为20KV。为了得到更加清晰准确的表面形貌,需要增加碳纤维的导电性,因此样品在进行测试前,先在离子溅射仪中进行喷金处理。The surface morphology of the recovered carbon fiber was observed and analyzed by using the FINA company's Quanta TM 250FEG model scanning electron microscope. Select high vacuum mode, the working distance is about 10mm, and the test acceleration voltage is 20KV. In order to obtain a clearer and more accurate surface topography, it is necessary to increase the conductivity of the carbon fiber, so the sample is subjected to gold spray treatment in an ion sputtering apparatus before being tested.
3.5原子力显微镜(AFM)测试3.5 atomic force microscope (AFM) test
选用美国布鲁克公司生产的ICON-PT-PKG型号扫描探针显微镜,对回收得到的碳纤维进行测试,可得到其表面微观形貌及起伏情况的二维和三维图。The ICON-PT-PKG model scanning probe microscope produced by Bruker Company of USA was used to test the recovered carbon fiber to obtain two-dimensional and three-dimensional images of the surface topography and undulation.
因此本实验的样品扫描范围选择4μm,采用轻敲模式,扫描速率为1.0Hz。为了保证测试成功率,碳纤维单丝的长度不应低于20mm。Therefore, the sample scanning range of this experiment was 4 μm, and the tapping mode was adopted, and the scanning rate was 1.0 Hz. In order to ensure the success rate of the test, the length of the carbon fiber monofilament should not be less than 20 mm.
利用NanoScope Analysis 1.8软件对图像进行分析计算,在软件的四种粗糙度表达公式中,选择Ra来表征粗糙度,其计算公式如下:The image was analyzed and calculated using NanoScope Analysis 1.8 software. In the four roughness expression formulas of the software, Ra was selected to characterize the roughness. The calculation formula is as follows:
Figure PCTCN2018075922-appb-000004
Figure PCTCN2018075922-appb-000004
式中N x—X轴的步数 N x - the number of steps in the X axis
N y—Y轴的步数 N y — the number of steps in the Y axis
3.6 X射线分析仪(XRD)3.6 X-ray analyzer (XRD)
选用德国Bruker公司生产的D8Advance型号高分辨率X射线分析仪,对回收碳纤维进行扫描检测,可以定性得到表面成分的晶体结构信息。采用Continuous PSD fast模式,工作电压为40KV,工作电流为200mA,测试铜靶辐射波长为154mm,扫描角度为10°~80°,步长为0.02°,每步扫描时间为0.2S。利用Jade5.0软件对图谱进行物相分析。The D8Advance high-resolution X-ray analyzer manufactured by Bruker of Germany was used to scan and recover the recovered carbon fiber, and the crystal structure information of the surface component can be qualitatively obtained. Using Continuous PSD fast mode, the working voltage is 40KV, the working current is 200mA, the test copper target radiation wavelength is 154mm, the scanning angle is 10°~80°, the step size is 0.02°, and the scanning time per step is 0.2S. The phase analysis of the map was performed using Jade 5.0 software.
3.7 X-射线光电子能谱(XPS)3.7 X-ray photoelectron spectroscopy (XPS)
选用ULVAC-PHI VPII型号光电子能谱仪,对回收得到的碳纤维进行先进行0eV~800eV范围的全谱扫描,得到其表面元素信息,再对C1s进行高分辨扫描,使用XPSPeak4.1软件对结果进行高斯函数和洛伦兹函数拟合,分析官能团的种类和含量情况信息。测试时,需要保证碳纤维平整的放置在测试台上。单色器的X射线源为Al靶,测试元素包括:C、O、Cl、N、Si、Ca,选择90°作为入射角。The ULVAC-PHI VPII model photoelectron spectrometer was used to perform the full-spectrum scanning of the recovered carbon fiber in the range of 0eV~800eV to obtain the surface element information, and then the C1s were scanned with high resolution, and the results were performed by XPSPeak4.1 software. Gaussian function and Lorentz function fitting, analysis of the type and content of functional groups. When testing, it is necessary to ensure that the carbon fiber is placed flat on the test bench. The X-ray source of the monochromator is an Al target, and the test elements include: C, O, Cl, N, Si, Ca, and 90° is selected as the incident angle.
示例4:电化学回收工艺设计Example 4: Electrochemical recovery process design
回收工艺步骤主要涉及三部分:(A)将准备好的碳纤维增强水泥基复合材料(板)放置在电解液;(B)对放置在电解液中的碳纤维增强水泥基复合材料通电,其中该碳纤维增强水泥基复合材料与电源的正极相连,并控制电流在合适大小范围内;和(C)通电反应适当时间(一般为8-240)小时后,自该电解液中取出生成的碳纤维回收物。在本发明提供的回收工艺中,根据不同分组,电流大小被控制在20mA和40mA;氯化钠浓度(重量百分比)被控制在2.0%和3.0%;催化剂HNO 3浓度被控制在0%、1%、3%和5%),共16种组测试样本。详细的样本分组和实验参数见表4.1。样本编号由电流大小、NaCl浓度和催化剂HNO 3浓度共同确定,比如样本编号“I20S 2.0H 1”,第一部分“I20”是指样本施加的电流是20mA,第二部分“S 2.0”是指电解液中NaCl浓度为2.0%,第三部分“H 1”是指每升电解液中添加的HNO 3浓度是1g。具体的实验参数及分组情况如表5.1所示。电化学回收周期为8天,回收结束后,将样本取出,除去表面的水泥基胶体,将得到的碳纤维清洗烘干, 然后进行各种测试。 The recycling process step mainly involves three parts: (A) placing the prepared carbon fiber reinforced cement-based composite material (plate) in the electrolyte; (B) energizing the carbon fiber reinforced cement-based composite material placed in the electrolyte, wherein the carbon fiber The reinforced cement-based composite material is connected to the positive electrode of the power source, and the current is controlled within a suitable size range; and (C) the electrification reaction is taken out from the electrolyte for a suitable time (usually 8-240 hours). In the recovery process provided by the present invention, the current magnitude is controlled at 20 mA and 40 mA according to different groupings; the sodium chloride concentration (% by weight) is controlled at 2.0% and 3.0%; the catalyst HNO 3 concentration is controlled at 0%, 1 %, 3%, and 5%), a total of 16 groups of test samples. Detailed sample grouping and experimental parameters are shown in Table 4.1. The sample number is determined by the current magnitude, NaCl concentration and catalyst HNO 3 concentration. For example, the sample number is “I20S 2.0 H 1 ”. The first part “I20” means that the current applied by the sample is 20 mA, and the second part “S 2.0 ” refers to electrolysis. The NaCl concentration in the liquid was 2.0%, and the third portion "H 1 " means that the concentration of HNO 3 added per liter of the electrolyte was 1 g. The specific experimental parameters and grouping conditions are shown in Table 5.1. The electrochemical recovery cycle was 8 days. After the recovery, the sample was taken out, the cement-based colloid on the surface was removed, and the obtained carbon fiber was washed and dried, and then subjected to various tests.
表4.1实验样本分组及参数Table 4.1 Experimental sample grouping and parameters
Figure PCTCN2018075922-appb-000005
Figure PCTCN2018075922-appb-000005
示例5:回收得到的碳纤维的清洗除胶Example 5: Cleaning and removing the carbon fiber
第一系列实验电化学回收周期为8天,第二系列实验电化学回收周期为4天。在回收过程,水泥基凝胶有少量溶解,溶液中和不锈钢片阴极上都有细微胶凝材料颗粒。回收结束后,从容液中取出试件,可以发现无机胶仍然与碳纤维连接在一起,如图2所示。因此,得到的碳纤维回收物为碳纤维和水泥基无机胶的混合物。换句话说,回收得到的碳纤维仍与水泥基无机胶连接在一起。然而,电化学回收反应结束后,水泥基凝胶材料会变得非常软,用硬直毛刷或刚性板即可将其轻易去除。然而,类似的强力剔除可能会使碳纤维表面残留有一层胶体,难以清除。为了更好地清除水泥基凝胶方法,可在碳纤维回收物表面每隔0.1mm以上插一个孔,然后用水压在0.1MPa以上的水流冲洗,冲刷时间为3秒以上,以除去水泥基无机胶。The first series of experimental electrochemical recovery cycles was 8 days, and the second series of experimental electrochemical recovery cycles was 4 days. In the recycling process, the cement-based gel has a small amount of dissolution, and there are fine cementitious material particles in the solution and on the cathode of the stainless steel sheet. After the recovery, the test piece was taken out from the liquid, and it was found that the inorganic glue was still connected to the carbon fiber, as shown in FIG. Therefore, the obtained carbon fiber recyclate is a mixture of carbon fiber and cement-based inorganic gum. In other words, the recovered carbon fiber is still joined to the cement-based inorganic glue. However, after the electrochemical recovery reaction, the cement-based gel material becomes very soft and can be easily removed with a hard straight brush or a rigid plate. However, a similar strong rejection may leave a layer of colloid on the surface of the carbon fiber that is difficult to remove. In order to better remove the cement-based gel method, a hole may be inserted every 0.1 mm or more on the surface of the carbon fiber recovery material, and then washed with a water flow of 0.1 MPa or more, and the scouring time is 3 seconds or more to remove the cement-based inorganic material. gum.
示例6:回收得到的碳纤维的性能测试Example 6: Performance test of recycled carbon fiber
6.1碳纤维回收物的硬度检测6.1 Hardness testing of carbon fiber recyclate
在电化学反应结束后,得到的碳纤维回收物包括碳纤维和无机胶,一般为板状或条状。涂层铅笔硬度测试方法测试其硬度。After the end of the electrochemical reaction, the resulting carbon fiber recyclate comprises carbon fibers and an inorganic gum, typically in the form of a plate or strip. The hardness of the coated pencil hardness test method was tested.
选用AIPLI仪器有限公司生产的QHQ-A型铅笔硬度计,根据规范 GB/T6739-2006/ISO15184:1998,在温度(23±2)℃和相对湿度(50±5)%条件下,置于表面结构一致的平板,铅笔在750g的负荷下以45°角向下压在复合材料表面上,以0.5mm/s~1mm/s的速度朝远离操作者的方向推动10mm,从铅笔最软级别9B开始,直至复合材料产生表面可见的内聚破坏,并使用精度为0.02mm的游标卡尺测量破坏深度。测试得到的复合材料详细硬度等级见表6.1。The QHQ-A pencil hardness tester produced by AIPLI Instrument Co., Ltd. was selected and placed on the surface according to the specification GB/T6739-2006/ISO15184:1998 under the conditions of temperature (23±2) °C and relative humidity (50±5)%. A uniform structure of the plate, the pencil is pressed down on the surface of the composite at a 45° angle under a load of 750g, pushing 10mm away from the operator at a speed of 0.5mm/s to 1mm/s, from the pencil softest level 9B Initially, the cohesive failure visible to the surface of the composite was observed and the depth of failure was measured using a vernier caliper with an accuracy of 0.02 mm. The detailed hardness grade of the tested composites is shown in Table 6.1.
表6.1复合材料样本硬度及内聚破坏深度Table 6.1 Composite material hardness and cohesive failure depth
Figure PCTCN2018075922-appb-000006
Figure PCTCN2018075922-appb-000006
注:硬部是指样本中硬度≥9H的部分,软部是指硬度<9H的部分。铅笔硬度计的软硬度从低到高依次为:9B-8B-7B-6B-5B-4B-3B-2B-1B-HB-F-H-2H-3H-4H-5H-6H-7H-8H-9HNote: The hard part refers to the part of the sample with hardness ≥ 9H, and the soft part refers to the part with hardness < 9H. The hardness of the pencil hardness tester from low to high is: 9B-8B-7B-6B-5B-4B-3B-2B-1B-HB-FH-2H-3H-4H-5H-6H-7H-8H- 9H
从表中可以看到,各分组碳纤维增强水泥基复合材料样本经电化学回收过程后,均有一定程度的变软,影响其软化程度最显著的因素是催化剂HNO 3,HNO 3浓度越大,复合材料受到的劣化程度越严重,硬度越低。H 0系列的样本硬度分为两部分,其硬部硬度远远大于9H,软部的硬度最低也为2B,并且软部面积很小,说明仅靠氯化钠溶液的电化学作用,碳纤维增强水泥基复合材料样本远没有达到破坏软化的程度,且软化不均匀。H 1系列中,I20S 2.0H 1和I40S 2.0H 1的样本仍然分为硬部和软部两部分,硬部的硬度分别为大于9H和9H,软部的硬度分别为5B和9B,I20S 3.0H 1和I40S 3.0H 1的样本硬度分别为7B和9B。以上结果表明NaCl浓度越大,碳纤维增强水泥基复合材料样本软化程度越大,体现在硬度上就是变得更软;同样的,电流增大会造成的碳纤维增强水泥基复合材料样本更软。H 3和H 5系列样本的硬度均小于9B,从测试造成的内聚破坏深度比较来看,同样能得到上述结论。 It can be seen from the table that the samples of each group of carbon fiber reinforced cement-based composite materials have a certain degree of softening after electrochemical recovery, and the most significant factor affecting the softening degree is the higher concentration of catalyst HNO 3 and HNO 3 . The more severe the degradation of the composite material, the lower the hardness. The hardness of the H 0 series is divided into two parts, the hardness of the hard part is much larger than 9H, the hardness of the soft part is also 2B, and the area of the soft part is small, indicating that the electrochemical action of the sodium chloride solution alone enhances the carbon fiber. Cement-based composite samples are far from achieving a degree of damage softening and softening unevenness. In the H 1 series, the samples of I20S 2.0 H 1 and I40S 2.0 H 1 are still divided into hard and soft parts. The hardness of the hard part is greater than 9H and 9H, respectively. The hardness of the soft part is 5B and 9B respectively. I20S 3.0 The sample hardness of H 1 and I40S 3.0 H 1 was 7B and 9B, respectively. The above results show that the higher the NaCl concentration, the greater the softening of the carbon fiber reinforced cement-based composite sample, and the softer the hardness. Similarly, the carbon fiber reinforced cement-based composite sample is softer due to the increase in current. The hardness of the H 3 and H 5 series samples is less than 9B, and the above conclusion can be obtained from the comparison of the depth of cohesive failure caused by the test.
附图之图3A至图3D所示为对碳纤维回收物的SEM扫描结果,其中图3A为未经电化学回收处理的碳纤维增强水泥基材料的水泥基与碳纤维相接的界面,其棱状沟槽结构相当完整和规则,能够与碳纤维形成强大的机械咬合作用,界面只有极小的孔洞,看不到裂缝 裂纹等缺陷。图3B是图3A中方框处的局部放大(放大10000倍),从中可以发现一些由水泥浆体和高分子聚合物相互交错嵌入的网络结构,这些结构增大了材料自身的强度和粘结性能。图3C是I40S 3.0H 1中碳纤维回收物的水泥基材料和碳纤维相接的界面,可以看到,菱形沟槽结构已经被纵横向的大裂缝所斩断分割成破碎的小单元,呈蓬松状,同时还有很多较大的裂纹孔洞分布其中,孔隙率剧烈增大,界面已经完全丧失了与碳纤维的机械咬合作用,粘结力大幅度下降。图D是图C中方框处的局部放大(放大10000倍),可以看到裂缝内部是白色的疏松状结构,水泥浆体和聚合物的相互嵌入网络结构已经被破坏,水泥基材料呈空洞化,碳纤维与水泥基界面的粘结力已经丧失。 3A to 3D are SEM scan results of the carbon fiber recyclate, wherein FIG. 3A is the interface between the cement-based and carbon fiber of the carbon fiber reinforced cement-based material which has not been electrochemically recovered, and the rib groove The groove structure is quite complete and regular, and it can form a strong mechanical bite with carbon fiber. The interface has only very small holes, and no cracks and other defects are seen. Fig. 3B is a partial enlargement (magnification 10000 times) at the box in Fig. 3A, from which a network structure in which the cement paste and the polymer are interlaced with each other can be found, which increase the strength and bonding property of the material itself. . Fig. 3C shows the interface between the cement-based material and the carbon fiber of the carbon fiber recyclate in I40S 3.0 H 1 . It can be seen that the rhombic groove structure has been divided into broken small units by the large cracks in the longitudinal and lateral directions, and is in a fluffy shape. At the same time, there are many large crack pores distributed, the porosity is increased sharply, the interface has completely lost the mechanical bite cooperation with carbon fiber, and the adhesion is greatly reduced. Figure D is a partial enlargement (magnification 10,000 times) at the box in Figure C. It can be seen that the inside of the crack is a white loose structure, the intercalated network structure of the cement paste and the polymer has been destroyed, and the cement-based material is hollowed out. The bond between the carbon fiber and the cement-based interface has been lost.
6.2碳纤维的回收量6.2 Carbon fiber recovery
从下表6.2中可以看到,碳纤维原丝的质量为841mg,此质量为30mm×100mm的碳纤维布条称量所得,需要指出的是,H 0系列由于该组碳纤维增强水泥基复合材料样本回收得到的碳纤维回收物硬度较大,不能轻易不费力气的去除水泥基材料,所以定义为碳纤维回收量为0g/L,在此表内不予列出。不同分组样本回收得到的碳纤维量有一定差异,直观的不同分组间碳纤维回收量,如图4所示。可以发现,碳纤维回收量随HNO 3浓度增大呈现先增后降趋势,HNO 3浓度为3g/L时,碳纤维回收量最大。在H 1组(1g/L)中,I20S 2.0和I40S 2.0的回收量明显低很多,只有233mg和286mg,原因是只回收到软部的碳纤维,而软部的面积在回收区占比较小。H 5系列样本的碳纤维回收较少,主要是因为碳纤维所受的劣化更大,表层剥落,变成很细很短毛丝,附着在水泥基材料上,在清洗阶段亦有损失。I40系列碳纤维回收量总体上比I20系列要低,S 3.0系列碳纤维回收量比S 2.0低(B为1g/L时除外),表明较大电流和较大氯化钠浓度造成碳纤维的劣化更大。不利于碳纤维回收。 As can be seen from Table 6.2 below, the carbon fiber precursor has a mass of 841 mg, and the carbon fiber cloth with a mass of 30 mm × 100 mm is weighed. It should be noted that the H 0 series is recovered from the sample of the carbon fiber reinforced cement-based composite material. The obtained carbon fiber recyclate has a large hardness and cannot easily remove the cement-based material without any effort, so it is defined as a carbon fiber recovery amount of 0 g/L, which is not listed in the table. The amount of carbon fiber recovered from different group samples is different, and the amount of carbon fiber recovered between different groups is intuitive, as shown in Figure 4. It can be found that the carbon fiber recovery amount increases first and then decreases with the increase of HNO 3 concentration, and the carbon fiber recovery amount is the largest when the HNO 3 concentration is 3g/L. In the H 1 group (1 g / L), the recovery of I20S 2.0 and I40S 2.0 was significantly lower, only 233 mg and 286 mg, because only the carbon fiber of the soft part was recovered, and the area of the soft part was relatively small in the recovery area. The H 5 series samples have less carbon fiber recovery, mainly because the carbon fiber is more deteriorated, the surface layer is peeled off, and it becomes very fine and short hair, which adheres to the cement-based material and is also lost during the cleaning stage. The I40 series carbon fiber recovery is generally lower than the I20 series, and the S 3.0 series carbon fiber recovery is lower than the S 2.0 (except when B is 1g/L), indicating that the larger current and larger sodium chloride concentration cause the carbon fiber to deteriorate more. . Not conducive to carbon fiber recycling.
表6.2不同参数条件下的碳纤维回收量Table 6.2 Carbon fiber recovery under different parameters
Figure PCTCN2018075922-appb-000007
Figure PCTCN2018075922-appb-000007
Figure PCTCN2018075922-appb-000008
Figure PCTCN2018075922-appb-000008
注:1)DB:表示破坏模式为无机脂层剥离破坏Note: 1) DB: indicates that the failure mode is the peeling of the inorganic fat layer.
2)CB:表示破坏模式为碳纤维与无机脂界面剥离破坏2) CB: indicates that the failure mode is the interface peeling damage between carbon fiber and inorganic grease
3)EB:表示破坏模式为碳纤维表层剥离破坏3) EB: indicates that the failure mode is carbon fiber surface peeling damage
为了确定电流在碳纤维增强水泥基复合材料样本的软化中是否起到作用,设置对比实验,将碳纤维增强水泥基复合材料样本分别泡浸在催化剂B(HNO 3)的剂量分别为1g/L、3g/L、5g/L、8g/L和10g/L剂量的2.0%NaCl溶液中,分别命名为S 2.0H 1、S 2.0H 3、S 2.0H 5、S 2.0H 8和S 2.0H 10,时间为8天。 In order to determine whether the current plays a role in the softening of carbon fiber reinforced cement-based composite samples, a comparative experiment was conducted to immerse the carbon fiber reinforced cement-based composite samples in the catalyst B (HNO 3 ) at a dose of 1 g/L and 3 g, respectively. In the 2.0% NaCl solution of /L, 5g/L, 8g/L and 10g/L doses, they were named S 2.0 H 1 , S 2.0 H 3 , S 2.0 H 5 , S 2.0 H 8 and S 2.0 H 10 , respectively. The time is 8 days.
碳纤维增强水泥基复合材料在泡浸前后有一定差异,颜色变浅,表面出现一些小孔洞,为了更精准评判催化剂B(HNO 3)的处理效果,进行硬度测试,结果见表6.3。从表中看到,处理后的复合材料硬度仍然很高,当HNO 3浓度达到10g/L时,复合材料硬度为3B,不借助机械工具不能把水泥胶体完成清除掉,并且长时间在高浓度催化剂B(HNO 3)溶液泡浸下,碳纤维性能会有很大劣化。表明电流在碳纤维增强水泥基复合材料软化中起到重要作用,电化学方法处理符合材料更加有效。 Carbon fiber reinforced cement-based composites have some differences before and after soaking, the color becomes lighter, and some small holes appear on the surface. In order to judge the treatment effect of catalyst B (HNO 3 ) more accurately, the hardness test is carried out, and the results are shown in Table 6.3. It can be seen from the table that the hardness of the treated composite is still very high. When the concentration of HNO 3 reaches 10g/L, the hardness of the composite is 3B. The cement colloid can not be removed without the aid of mechanical tools, and the concentration is high for a long time. When the catalyst B (HNO 3 ) solution is soaked, the carbon fiber properties are greatly deteriorated. It indicates that current plays an important role in the softening of carbon fiber reinforced cement-based composites, and electrochemical treatment is more effective in conforming with materials.
表6.3 B电解液处理后复合材料硬度Table 6.3 Hardness of composite after B electrolyte treatment
Figure PCTCN2018075922-appb-000009
Figure PCTCN2018075922-appb-000009
6.3样本电压检测6.3 sample voltage detection
从图5可以看到,所有样本的电压在电化学回收周期基本保持稳定,没有很大的波动。不同分组样本电压有一定差异,H 0(0g/L)组样本的电压最高,相对波动最大,原因可能是没有催化剂HNO 3对碳纤维增强水泥基复合材料样本的软化作用比较慢,孔隙率很小,样本导电性能不好,因此电压较高,波动较大。H 5系列样本的电压低于H 0系列,但仍然比较高,在H 5系列中,样本水泥基材料的破坏非常严重,已经作用到碳纤维,其电压较高可能是与碳纤维的劣化导致电阻增大有关。H 3(3g/L)与H 1(1g/L)组样本电压较低,这是由于电化学作用对碳纤维增强水泥基复合材料作用比较缓和,碳纤维的劣化很轻微,导电性能较好。在总体上,I40系列样本电压比I20系列大,S 3.0系列样本电压比S 2.0系列大,表明电压和NaCl浓度越大,其阻值越大,因而电压越大。 As can be seen from Figure 5, the voltages of all samples remained substantially stable during the electrochemical recovery cycle without significant fluctuations. The sample voltages of different groups are different. The H 0 (0g/L) group has the highest voltage and the highest relative fluctuation. The reason may be that the catalyst HNO 3 has a slower softening effect on the carbon fiber reinforced cement matrix composite sample and the porosity is very small. The conductivity of the sample is not good, so the voltage is high and the fluctuation is large. The voltage of the H 5 series sample is lower than the H 0 series, but it is still relatively high. In the H 5 series, the damage of the sample cement-based material is very serious and has been applied to the carbon fiber. The higher voltage may be caused by the deterioration of the carbon fiber and the increase in resistance. Big related. The sample voltages of H 3 (3g/L) and H 1 (1g/L) groups are lower, which is due to the milder effect of electrochemical action on carbon fiber reinforced cement-based composites, the deterioration of carbon fibers is slight, and the electrical conductivity is better. In general, the I40 series sample voltage is larger than the I20 series, and the S 3.0 series sample voltage is larger than the S 2.0 series, indicating that the larger the voltage and the NaCl concentration, the larger the resistance value, and thus the higher the voltage.
从表5.5可以看到,回收得到的碳纤维直径没有变化,说明在电化学回收过程碳纤维虽然受到电化学氧化及酸的腐蚀等作用,但是碳纤维表面基本没有片层剥落。经检测,碳纤维原丝的单丝拉伸强度为3588MPa,回收得到的碳纤维中I20S 2.0H 1的拉伸强度最高为 3072MPa,达到碳纤维原丝的85.62%;I40S 3.0H 5的拉伸强度最低为2162MPa,仅为碳纤维原丝的60.26%。其他回收得到的碳纤维的单丝拉伸强度相比碳纤维原丝均出现不同程度的下降,详见图6。 It can be seen from Table 5.5 that the diameter of the recovered carbon fiber does not change, indicating that although the carbon fiber undergoes electrochemical oxidation and acid corrosion during the electrochemical recovery process, there is substantially no peeling of the surface of the carbon fiber. The tensile strength of the monofilament of the carbon fiber precursor was 3588 MPa, and the tensile strength of I20S 2.0 H 1 in the recovered carbon fiber was 3072 MPa, which was 85.62% of the carbon fiber precursor; the tensile strength of I40S 3.0 H 5 was the lowest. 2162MPa, only 60.26% of carbon fiber precursor. The tensile strength of the monofilament of other recycled carbon fibers showed a different degree of decline compared to the carbon fiber precursor, as shown in Figure 6.
如附图之图6所示,回收得到的碳纤维的单丝拉伸强度随HNO 3浓度增大而呈下降趋势,在0~3(g/L)的HNO 3浓度区间,碳纤维的拉伸强度下降幅度较小,3~5(g/L)的HNO 3浓度区间碳纤维拉伸强度急剧下降,说明HNO 3浓度越高,对碳纤维造成的劣化越严重,尤其是当HNO 3浓度超过3(g/L)之后。当HNO 3浓度为1(g/L)和3(g/L)时,不同参数作用下的碳纤维间拉伸强度差值不大,H 1系列碳纤维拉伸强度在2987MPa~3072MPa之间,H 3系列碳纤维拉伸强度在2898MPa~2974MPa范围区间,I20系列碳纤维拉伸强度比I40系列要高,S 2.0系列碳纤维拉伸强度比S 3.0强度要高;当HNO 3浓度为5(g/L)时,不同参数间碳纤维的强度差值比较小,但是仍然是小电流系列样本比大电流系列样本高,低氯化钠浓度系列样本比高浓度系列样本高。 As shown in FIG. 6 of the drawings, the recycled carbon fiber resulting single filament tensile strength with increasing concentration of HNO 3 decreased tensile strength in 0 ~ 3 (g / L) concentration of HNO 3 in section, of carbon fibers The decrease is small, and the tensile strength of carbon fiber in the range of HNO 3 concentration of 3 to 5 (g/L) drops sharply, indicating that the higher the concentration of HNO 3 , the more serious the deterioration of carbon fiber, especially when the concentration of HNO 3 exceeds 3 (g). /L) After. When the concentration of HNO 3 is 1 (g/L) and 3 (g/L), the difference in tensile strength between carbon fibers under different parameters is not large, and the tensile strength of H 1 series carbon fibers is between 2987 MPa and 3072 MPa. The tensile strength of 3 series carbon fiber ranges from 2898MPa to 2974MPa. The tensile strength of I20 series carbon fiber is higher than that of I40 series. The tensile strength of S 2.0 series carbon fiber is higher than that of S 3.0 ; when the concentration of HNO 3 is 5 (g/L) At the same time, the difference in the strength of the carbon fiber between the different parameters is relatively small, but the sample of the small current series is still higher than the sample of the high current series, and the sample of the low sodium chloride concentration is higher than the sample of the high concentration series.
6.4回收得到的碳纤维的界面剪切性能6.4 Interfacial shear properties of recycled carbon fibers
从表6.4可以看到,碳纤维原丝与无机脂的界面剪切强度为27.09MPa,破坏模式为DB,回收得到的碳纤维的界面剪切强度较大,除了H 5系列,其他系列的样本剪切强度都大于等于碳纤维原丝,破坏模式与HNO 3浓度相关,H 1系列样本的破坏模式为DB,H 3系列样本破坏模式为CB,H 5系列样本的破坏模式为EB,随着HNO 3浓度的增大,破坏位置从无机脂层转移到界面层再到碳纤维表层。 It can be seen from Table 6.4 that the interfacial shear strength of carbon fiber precursor and inorganic grease is 27.09 MPa, the failure mode is DB, and the interfacial shear strength of the recovered carbon fiber is large, except for the H 5 series, other series of sample shearing The strength is greater than or equal to the carbon fiber precursor, the failure mode is related to the HNO 3 concentration, the failure mode of the H 1 series sample is DB, the destruction mode of the H 3 series sample is CB, and the failure mode of the H 5 series sample is EB, with the concentration of HNO 3 The increase in the location of the damage from the inorganic lipid layer to the interface layer to the carbon fiber surface.
表6.4回收碳纤维的界面剪切强度Table 6.4 Interfacial shear strength of recycled carbon fiber
Figure PCTCN2018075922-appb-000010
Figure PCTCN2018075922-appb-000010
注:1)DB:表示破坏模式为环氧树脂层剥离破坏Note: 1) DB: indicates that the failure mode is the epoxy layer peeling damage
2)CB:表示破坏模式为碳纤维与环氧树脂界面剥离破坏2) CB: indicates that the failure mode is the peeling failure of the interface between carbon fiber and epoxy resin
3)EB:表示破坏模式为碳纤维表层剥离破坏3) EB: indicates that the failure mode is carbon fiber surface peeling damage
从图7可以看到,回收得到的碳纤维的界面剪切强度随HNO 3浓度增大而下降,但是H 1和H 3系列回收得到的碳纤维比原丝剪切强度大,说明在较低浓度的B条件下的电化学氧化能够提高剪切强度。从图8A可以看到,碳纤维原丝的破坏模式为DB,无机脂层被剥离,碳纤维表面粘结着一层光滑的树脂;图8B和图8C分别是I20S 2.0H 1和I40S 2.0H 1的破坏图像,虽然破坏模式仍然是DB,但是碳纤维表面粘结的树脂层粗糙呈凹凸状,尤其是I20S 2.0H 1样本,说明H 1系列的碳纤维与无机脂的粘结力更强,可能是由于低浓度的B下,碳纤维表面的微观结构被氧化刻蚀得更好,机械咬合作用更强;在图8D和图8E中,I20S 2.0H 3和I40S 2.0H 3的破坏模式虽然是CB,但是剥离破坏后,碳纤维表面粘结有针状的细长无机脂,针状树脂不但增大破坏表面积,而且起到类似钢筋月牙肋的作用,极大提高机械咬合力,增大与无机脂的粘结性能,因而S 2.0系列样本的剪切强度仍然比碳纤维原丝高。在HNO 3浓度为1(g/L)和3(g/L)时,I20系列样本剪切强度比I40系列高,I20S 3.0H 1;S 2.0系列样本剪切强度比S 3.0系列高;在H 5系列,小电流与B低浓度作用的样本剪切强度更大,但是由于过度的氧化刻蚀,电流与B参数对剪切强度的影响非常小,从图8F和图8G看到,I20S 2.0H 5的剥离模式为CB,碳纤维表面没有树脂残留,看到表面的纵向沟槽结构,表明碳纤维与无机脂的粘结性能下降;I40S 2.0H 5的破坏模式为EB,可以看到,碳纤维表面被剥离了小部分表皮,可能是该处表皮已被氧化成脆弱片层,与碳纤维本体不再为牢固的整体;表明HNO 3浓度为5%时,回收得到的碳纤维受到较严重的氧化和腐蚀作用,降低了碳纤维表面粘结性能。 It can be seen from Fig. 7 that the interfacial shear strength of the recovered carbon fiber decreases with the increase of the HNO 3 concentration, but the carbon fiber recovered by the H 1 and H 3 series is larger than the shear strength of the original yarn, indicating that it is at a lower concentration. Electrochemical oxidation under B conditions can increase the shear strength. As can be seen from Fig. 8A, the carbon fiber precursor has a failure mode of DB, the inorganic lipid layer is peeled off, and the surface of the carbon fiber is bonded with a smooth resin; Figs. 8B and 8C are I20S 2.0 H 1 and I40S 2.0 H 1 , respectively. Destroying the image, although the failure mode is still DB, the resin layer bonded on the surface of the carbon fiber is rough and uneven, especially the I20S 2.0 H 1 sample, indicating that the carbon fiber of the H 1 series is more strongly bonded to the inorganic grease, probably due to At low concentrations of B, the microstructure of the carbon fiber surface is oxidized and etched better, and the mechanical bite is stronger; in Figures 8D and 8E, the failure modes of I20S 2.0 H 3 and I40S 2.0 H 3 are CB, but After peeling and ruining, the surface of the carbon fiber is bonded with a needle-like slender inorganic grease. The acicular resin not only increases the surface area of the fracture, but also acts like a steel rib, greatly improves the mechanical bite force and increases the adhesion to the inorganic grease. Knot performance, so the shear strength of the S 2.0 series samples is still higher than that of carbon fiber strands. When the concentration of HNO 3 is 1 (g/L) and 3 (g/L), the shear strength of I20 series samples is higher than that of I40 series, I20S 3.0 H 1 ; the shear strength of S 2.0 series samples is higher than that of S 3.0 series; In the H 5 series, the shear strength of the sample with small current and low B concentration is greater, but due to excessive oxidation etching, the influence of current and B parameters on shear strength is very small. See Figure 8F and Figure 8G for I20S. The peeling mode of 2.0 H 5 is CB, there is no resin residue on the surface of carbon fiber, and the longitudinal groove structure of the surface is seen, indicating that the bonding performance of carbon fiber and inorganic grease is degraded; the failure mode of I40S 2.0 H 5 is EB, it can be seen that carbon fiber The surface is peeled off a small portion of the skin, which may have been oxidized into a fragile sheet, which is no longer a solid whole with the carbon fiber body; indicating that the recovered carbon fiber is subjected to more severe oxidation when the HNO 3 concentration is 5%. Corrosion reduces the bonding properties of carbon fiber surface.
示例7:回收得到的碳纤维的检测Example 7: Detection of recovered carbon fiber
7.1 SEM扫描7.1 SEM scan
经检测发现,S 2.0系列和S 3.0系列回收得到的碳纤维的微观形貌差别非常小,所以在此只列出S 2.0系列回收得到的碳纤维的SEM图像。从图9A可以看到,碳纤维原丝表面非常光滑平整,没有看到裂纹裂缝凹坑等缺陷。经回收得到的碳纤维表面附着有少量的凝胶颗粒,这是清洗不够彻底造成的残留。从图9B和图9C中看到,I20S 2.0H 1和I40S 2.0H 1回收得到的碳纤维表面除了附着有极少量的水泥凝胶外,并未看到裂纹裂缝凹坑等缺陷,十分完整,表明在1(g/L)浓度的B条件下,电化学回收过程对回收得到的碳纤维并未造成严重的氧化劣化,所以该系列回收得到的碳纤维的拉伸强度下降幅度不大。从图9D和图9E发现,I20S 2.0H 3和I40S 2.0H 3回收得到的碳纤维表面很干净,极少水泥凝胶颗粒残留,但是在个别根数的碳纤维表面发现有横向裂纹,在裂纹处形成薄弱层,造成碳纤维拉伸强度下降,因此H 3系列回收得到的碳纤维拉伸强度比H 1系列低。表明在3g/L浓度的催化剂B条 件下,碳纤维在回收过程受到的氧化劣化程度增加。从图9F和图9G看到,I20S 2.0H 5和I40S 2.0H 5回收得到的碳纤维表面的水泥凝胶颗粒较多,在碳纤维表面发现有纵向裂缝和横向裂纹,且深度不浅,减小了碳纤维的受力截面,因此H 5系列回收得到的碳纤维的拉伸强度严重下降,只达到碳纤维原丝强度的60.26%~66.64%。说明在5g/L浓度的催化剂B条件下,碳纤维在回收过程受到了严重的氧化劣化。对比图10中I20系列与I40系列回收得到的碳纤维图像,发现I40系列回收得到的碳纤维的表面缺陷更多,说明大电流作用使回收得到的碳纤维受到的损伤更严重。 It has been found that the difference in the microscopic morphology of the carbon fibers recovered from the S 2.0 series and the S 3.0 series is very small, so only the SEM images of the carbon fibers recovered in the S 2.0 series are listed here. As can be seen from Fig. 9A, the surface of the carbon fiber precursor was very smooth and flat, and no defects such as crack crack pits were observed. A small amount of gel particles adhere to the surface of the recovered carbon fiber, which is a residue caused by insufficient cleaning. It can be seen from Fig. 9B and Fig. 9C that the surface of the carbon fiber recovered by I20S 2.0 H 1 and I40S 2.0 H 1 has no defects such as crack cracks and pits, except for the adhesion of a very small amount of cement gel. Under the condition of B at a concentration of 1 (g/L), the electrochemical recovery process does not cause serious oxidative degradation on the recovered carbon fibers, so the tensile strength of the carbon fibers recovered in this series does not decrease much. It is found from Fig. 9D and Fig. 9E that the surface of the carbon fiber recovered by I20S 2.0 H 3 and I40S 2.0 H 3 is very clean, and little cement gel particles remain, but transverse cracks are found on the surface of individual carbon fibers, forming at the cracks. The weak layer causes the tensile strength of the carbon fiber to decrease, so the tensile strength of the carbon fiber recovered by the H 3 series is lower than that of the H 1 series. It is shown that under the condition of Catalyst B at a concentration of 3 g/L, the degree of oxidative degradation of the carbon fiber during the recovery process is increased. As seen from Fig. 9F and Fig. 9G, the surface of the carbon fiber recovered by I20S 2.0 H 5 and I40S 2.0 H 5 has more cement gel particles, and longitudinal cracks and transverse cracks are found on the surface of the carbon fiber, and the depth is not shallow, which is reduced. The tensile strength of the carbon fiber recovered by the H 5 series is seriously reduced, and only the strength of the carbon fiber precursor is 60.26% to 66.64%. It is indicated that under the condition of Catalyst B at a concentration of 5 g/L, the carbon fiber is subjected to severe oxidative degradation during the recovery process. Comparing the carbon fiber images recovered from the I20 series and the I40 series in Fig. 10, it was found that the carbon fibers recovered by the I40 series had more surface defects, indicating that the large current action caused the damage of the recovered carbon fibers to be more serious.
7.2 AFM扫描7.2 AFM scan
碳纤维的表面微观形貌对其界面粘结性能起到非常重要的影响,由粗糙度和形貌结构共同表征,碳纤维原丝和回收得到的碳纤维的AFM扫描测试结果分别见表7.1和图10,需要指出的是,S 2.0系列和S 3.0系列的回收得到的碳纤维在粗糙度和形貌结构上差别不大,所以在此只列出S 2.0系列回收得到的碳纤维AFM图像。 The surface topography of carbon fiber plays a very important role in the interfacial adhesion properties. It is characterized by roughness and morphology structure. The AFM scanning test results of carbon fiber precursor and recovered carbon fiber are shown in Table 7.1 and Figure 10, respectively. It should be noted that the recycled carbon fibers of the S 2.0 series and the S 3.0 series have little difference in roughness and morphology, so only the carbon fiber AFM images recovered by the S 2.0 series are listed here.
表7.1回收得到的碳纤维的粗糙度Table 7.1 Roughness of recovered carbon fiber
Figure PCTCN2018075922-appb-000011
Figure PCTCN2018075922-appb-000011
从图10A和图10B可以看到,碳纤维原丝表面很光滑,没有纵向沟槽结构,几乎没有表皮凸起结构,计算得到的粗糙度为144nm。从图10C至图10F可以发现,在H 1碳纤维系列,由于回收过程的氧化刻蚀作用,碳纤维表面出现明显的纵向沟槽结构和表皮凸起结构, 这些精细结构起到类似钢筋月牙肋的作用,极大的提高碳纤维与无机脂的机械咬合作用,增大碳纤维表面粗糙度,I20S 2.0H 1和I40S 2.0H 1的粗糙度分别为180nm和178nm,增加比表面积,改善浸润性,提高了界面粘结性能,因此,H 1系列回收得到的碳纤维剪切强度远高于碳纤维原丝。从图10G至图10J看到,当HNO 3浓度增大到3时,碳纤维表面仍然有纵向沟槽结构,但是比H 1系列弱,I20S 2.0H 3碳纤维表面的凸起结构增多,而I40S 2.0H 3只有不同明显的纵向沟槽结构,计算得到的粗糙度分别为208nm和162nm,纵向沟槽结构变弱,导致碳纤维表面的机械咬合作用下降,因而H 3系列回收得到的碳纤维界面剪切强度比H 1系列低,但仍然高于碳纤维原丝,表明HNO 3浓度增大,造成碳纤维受到的氧化刻蚀等劣化增强,导致界面剪切强度削弱。从图10K至图10N看到,HNO 3浓度继续增大到5时,I20S 2.0H 5和I40S 2.0H 5碳纤维表面几乎看不到纵向沟槽结构,只有错杂的凸起结构,计算得到的粗糙度分别为104nm和121nm,需要指出的是,I40S 2.0H 5的纵向凹槽为生产时造成,并非氧化刻蚀所致。过度的氧化刻蚀使活性碳粒脱落,无法形成纵向沟槽结构,碳纤维的机械咬合力急剧下降,导致H 5系列回收得到的碳纤维剪切强度下降,略低于碳纤维原丝,并且严重氧化的凸起机构与碳纤维本体间的粘结变弱,在进行树脂微滴拨出时,容易发生剥离,造成EB破坏模式。上述表明,当HNO 3浓度较低时,电化学回收过程的小量氧化刻蚀会增大碳纤维的界面剪切强度,而HNO 3浓度增大到一定程度时,过量的氧化刻蚀反而使碳纤维的界面剪切强度降低。 As can be seen from Fig. 10A and Fig. 10B, the surface of the carbon fiber precursor is very smooth, has no longitudinal groove structure, has almost no skin convex structure, and has a calculated roughness of 144 nm. From Fig. 10C to Fig. 10F, it can be found that in the H 1 carbon fiber series, due to the oxidative etching action of the recycling process, a significant longitudinal groove structure and a skin convex structure appear on the surface of the carbon fiber, and these fine structures function like steel ribs. Greatly improve the mechanical bite of carbon fiber and inorganic grease, increase the surface roughness of carbon fiber, the roughness of I20S 2.0 H 1 and I40S 2.0 H 1 are 180nm and 178nm respectively, increase the specific surface area, improve the wettability and improve the interface. Bonding properties, therefore, the shear strength of the carbon fiber recovered from the H 1 series is much higher than that of the carbon fiber precursor. It can be seen from Fig. 10G to Fig. 10J that when the concentration of HNO 3 is increased to 3, the surface of the carbon fiber still has a longitudinal groove structure, but is weaker than the H 1 series, and the convex structure on the surface of the I20S 2.0 H 3 carbon fiber is increased, and the I40S 2.0 is increased. H 3 has only different longitudinal groove structures, and the calculated roughness is 208 nm and 162 nm, respectively. The longitudinal groove structure becomes weak, resulting in a decrease in the mechanical bite of the carbon fiber surface. Therefore, the shear strength of the carbon fiber interface recovered by the H 3 series is obtained. It is lower than the H 1 series, but still higher than the carbon fiber precursor, indicating that the concentration of HNO 3 is increased, causing the carbon fiber to undergo oxidative etching and the like to be deteriorated, resulting in weakened interface shear strength. It can be seen from Fig. 10K to Fig. 10N that when the HNO 3 concentration continues to increase to 5, the longitudinal groove structure is hardly visible on the surface of the I20S 2.0 H 5 and I40S 2.0 H 5 carbon fibers, and only the miscellaneous convex structure is obtained, and the calculated roughness is obtained. The degrees are 104 nm and 121 nm, respectively. It should be noted that the longitudinal grooves of the I40S 2.0 H 5 are produced during production, not by oxidative etching. Excessive oxidative etching causes the activated carbon particles to fall off, and the longitudinal groove structure cannot be formed. The mechanical bite force of the carbon fiber drops sharply, resulting in a decrease in the shear strength of the carbon fiber recovered by the H 5 series, slightly lower than that of the carbon fiber precursor, and severely oxidized. The adhesion between the convex mechanism and the carbon fiber body is weakened, and peeling is likely to occur when the resin droplets are dialed out, resulting in an EB failure mode. The above shows that when the concentration of HNO 3 is low, the small amount of oxidative etching in the electrochemical recovery process increases the interfacial shear strength of the carbon fiber, and when the concentration of HNO 3 increases to a certain extent, the excessive oxidation etching causes the carbon fiber to The interface shear strength is reduced.
7.3 XPS扫描7.3 XPS scanning
经检测,回收得到的碳纤维的XPS扫描全谱及C1s高分辨窄谱见图11A至图11H,左列是样本的扫描全谱。从扫描全谱图可以看到,图中主要有五种峰,即两个主峰:C(284.6eV)和O(532.0eV);三个次要峰:Si(99.5eV)、Cl(199.8eV)和Ca(347eV)。碳纤维原丝的表面基本元素为碳和氧,检测出来的少量硅、氯和钙是在实验过程中的引入。VCF和I20S 2.0组回收得到的碳纤维表面具体的化学元素含量情况见表7.2。 After detection, the XPS scanning full spectrum and the C1s high resolution narrow spectrum of the recovered carbon fiber are shown in Fig. 11A to Fig. 11H, and the left column is the scanning full spectrum of the sample. It can be seen from the scanning full spectrum that there are five main peaks in the figure, namely two main peaks: C (284.6 eV) and O (532.0 eV); three secondary peaks: Si (99.5 eV), Cl (199.8 eV). ) and Ca (347eV). The basic elements of the carbon fiber precursor are carbon and oxygen, and the small amount of silicon, chlorine and calcium detected is introduced during the experiment. The specific chemical element content of the carbon fiber surface recovered from the VCF and I20S 2.0 groups is shown in Table 7.2.
表7.2 VCF和I20S 2.0组回收得到的碳纤维表面元素含量(%) Table 7.2 Surface Element Content of Carbon Fiber Recovered by VCF and I20S 2.0 Group (%)
Figure PCTCN2018075922-appb-000012
Figure PCTCN2018075922-appb-000012
从表中看到,碳纤维原丝表面的碳含量高达79.3%,氧含量为20.7%,没有检测到其他元素含量。所有回收得到的碳纤维表面的碳含量都比较接近,相比碳纤维原丝大概下降 了10%,氧含量则有一定程度上升;从氧碳比来看,回收得到的碳纤维远高于碳纤维原丝的0.2610,在三种HNO 3浓度梯度中,H 3的氧碳比最高,接着是H 5,最低是H 1,说明了H 3是区域最佳浓度,能够引入更多的氧,获得更大的表面活性,增强与无机脂的化学键结合能力。从氯含量来看,HNO 3浓度增大会提高碳纤维表面氯含量。所有碳纤维样本表面都引入了一定量的钙,这可能是水泥基材料在碳纤维表面的残留。此外,I20S 2.0H 1碳纤维表面监测出3.4%的硅含量。利用软件XPSPeak4.1,将C1s高分辨窄谱依据结合能分为以下六种化学键峰进行高斯洛伦茨拟合:石墨态C~C(284.4eV)、非晶态C~C(284.8eV)、C=O(285.5eV)、C~O(286.2eV)、C~Cl(287.2)和O~C=O(288.4eV)。C1s分峰拟合见图5.15右列,需要指出的是,碳纤维原丝的C1s为双峰,并且在288eV峰位后没有面积,所以拟合得出的结果显示,碳纤维原丝表面不含O~C=O键,其他碳碳和碳氧化学键峰位均出现偏移,表明碳纤维原丝表面活性不好。而回收得到的碳纤维表面的C~Cl键含量为零,说明回收得到的碳纤维表面的氯以吸附状态存在,并非以化学键结合。具体的回收得到的碳纤维表面官能团含量见表7.3。 It can be seen from the table that the carbon fiber surface has a carbon content of 79.3% and an oxygen content of 20.7%, and no other element content is detected. The carbon content of all recovered carbon fiber surfaces is relatively close, which is about 10% lower than that of carbon fiber precursors, and the oxygen content is increased to some extent. From the oxygen-carbon ratio, the recovered carbon fibers are much higher than the carbon fiber precursors. 0.2610, in the three HNO 3 concentration gradients, H 3 has the highest oxygen-to-carbon ratio, followed by H 5 , and the lowest is H 1 , indicating that H 3 is the optimal concentration in the region and can introduce more oxygen to obtain a larger Surface activity enhances the chemical bonding ability with inorganic lipids. From the perspective of chlorine content, an increase in the concentration of HNO 3 increases the chlorine content of the carbon fiber surface. A certain amount of calcium is introduced on the surface of all carbon fiber samples, which may be the residue of the cement-based material on the surface of the carbon fiber. In addition, the I20S 2.0 H 1 carbon fiber surface monitored a 3.4% silicon content. Using the software XPSPeak4.1, the C1s high-resolution narrow spectrum is divided into the following six chemical bond peaks according to the binding energy: Gauss Lorenz fitting: graphite state C~C (284.4eV), amorphous C~C (284.8eV) C=O (285.5 eV), C~O (286.2 eV), C-Cl (287.2), and O-C=O (288.4 eV). The C1s peak fitting is shown in the right column of Figure 5.15. It should be noted that the C1s of the carbon fiber precursor is double-peak and there is no area after the 288eV peak, so the fitting results show that the surface of the carbon fiber precursor does not contain O. ~C=O bond, the other carbon-carbon and carbon oxidation bond peaks are offset, indicating that the carbon fiber precursor surface activity is not good. The content of the C-Cl bond on the surface of the recovered carbon fiber is zero, indicating that the chlorine on the surface of the recovered carbon fiber exists in an adsorbed state, and is not chemically bonded. The specific recovered carbon fiber surface functional group content is shown in Table 7.3.
表7.3 VCF和I20S 2.0组回收得到的碳纤维表面官能团含量(%) Table 7.3 Carbon fiber surface functional group content (%) recovered from VCF and I20S 2.0 groups
Figure PCTCN2018075922-appb-000013
Figure PCTCN2018075922-appb-000013
从表中发现,碳纤维原丝表面的石墨态和非晶态C~C键总量为51.1%,I20S 2.0H 1的碳~碳键含量稍微上升为52.8%,I20S 2.0H 3和I20S 2.0H 5则出现下降,分别为49.4%和48.4%。在碳氧键方面,回收得到的碳纤维的C~O键出现大幅度下降,下降量从大到小排序为:H 3>H 5>H 1;回收得到的碳纤维的C=O键则出现小幅度的下降,在强亲水性官能团O~C=O键含量上,相比碳纤维原丝的含量为零,回收得到的碳纤维的含量很高,并且H 3>H 5>H 1。上述情况表明,碳纤维在回收过程经历了一定程度的氧化,表面含氧量增大,提高了表面活性,并且O~C=O键出现,极大提高了碳纤维与无机脂的化学键结合能力;从回收得到的碳纤维的氧碳比和官能团含量来看,HNO 3浓度为1.0g/L时,碳纤维氧化程度过低,当HNO 3浓度为3.0g/L时,碳纤维氧化程度最好,增大HNO 3浓度只是使碳纤维表面C=O键增多。 It is found from the table that the total amount of graphite and amorphous C-C bonds on the surface of carbon fiber precursor is 51.1%, and the carbon-carbon bond content of I20S 2.0 H 1 is slightly increased to 52.8%, I20S 2.0 H 3 and I20S 2.0 H 5 decreased, 49.4% and 48.4% respectively. In terms of carbon-oxygen bonds, carbon fiber obtained recycled C ~ O bond of a major decline, decrease of the amount of descending order: H 3> H 5> H 1; recovered carbon fibers C = O bond appeared small The decrease in the amplitude is zero in the content of the strongly hydrophilic functional group O to C=O, compared to the content of the carbon fiber precursor, and the recovered carbon fiber is high in content, and H 3 >H 5 >H 1 . The above situation indicates that the carbon fiber undergoes a certain degree of oxidation during the recovery process, the surface oxygen content increases, the surface activity is increased, and the O~C=O bond appears, which greatly improves the chemical bonding ability of the carbon fiber and the inorganic grease; The oxygen-carbon ratio and functional group content of the recovered carbon fiber showed that the degree of oxidation of carbon fiber was too low when the concentration of HNO 3 was 1.0 g/L. When the concentration of HNO 3 was 3.0 g/L, the degree of oxidation of carbon fiber was the best, and HNO was increased. The concentration of 3 only increases the C=O bond on the surface of the carbon fiber.
7.4 XRD7.4 XRD
参考本发明附图之图18A和图18B,其主要展示了I20系列和I40系列于不同温度梯 度所回收的碳纤维的XRD图谱,其中所有回收碳纤维的XRD光谱只有一个强衍射峰,峰位在2θ=26°附近,经过物相检索,判定为C,表明在电化学回收过程,碳纤维表面并没有引入其他晶体结构化合物。Referring to Figures 18A and 18B of the accompanying drawings, the XRD patterns of the carbon fibers recovered by the I20 series and the I40 series at different temperature gradients are mainly shown, wherein the XRD spectrum of all recovered carbon fibers has only one strong diffraction peak and the peak position is at 2? Near =26°, after phase retrieval, it was judged as C, indicating that other crystal structure compounds were not introduced into the surface of the carbon fiber during the electrochemical recovery process.
值得一提的是,从图中可以进一步观察发现,XRD光谱基本呈温度越高,特征峰衍射强度越高,峰愈加尖锐趋势,表明回收温度越高,碳纤维结晶度越好,晶粒更加小。Papirer E的研究表明,碳纤维表面晶粒越小,其表面棱角和边沿的不饱和C原子愈多,表面活性愈高,可以在一定程度上改善碳纤维与树脂的粘结性能,以及提高碳纤维的拉伸强度。I20系列碳纤维比I40系列特征峰好,表明小电流作用对碳纤维的石墨块状结构影响更小,更有利于回收碳纤维的力学性能。It is worth mentioning that, from the figure, it can be further observed that the XRD spectrum is basically higher in temperature, the higher the diffraction intensity of the characteristic peak, the sharper the peak, indicating that the higher the recovery temperature, the better the crystallinity of carbon fiber and the smaller the crystal grain. . Papirer E's research shows that the smaller the surface of carbon fiber, the more unsaturated C atoms on the surface edges and edges, the higher the surface activity, which can improve the bonding performance of carbon fiber and resin to some extent, and improve the pulling of carbon fiber. Stretch strength. The I20 series carbon fiber has better characteristic peak than the I40 series, indicating that the small current effect has less influence on the graphite block structure of the carbon fiber, and is more conducive to recovering the mechanical properties of the carbon fiber.
示例8:温度对电化学回收碳纤维的影响Example 8: Effect of temperature on electrochemically recovered carbon fiber
与其它化学反应相似,电化学法回收碳纤维的化学反应过程也应当有其合适的反应条件。本发明通过下述实验结果,确定本发明电化学回收方法的合适温度。同样地,多组样本(如下表6.1所示)被用于测试合适反应温度,其中被选用的电流强度分别为20mA和40mA,NaCl浓度为2.0(%),HNO 3剂量为3.0g/L,温度梯度为排除了收率过低的极端温度(极低,如0℃以下,和100℃以上温度)的四个温度梯度,共6组。样本编号由作用电流、NaCl浓度、催化剂HNO 3浓度和温度梯度共同确定,比如样本编号“I20S 2.0H 3T 40”,第一部分“I20”是指样本施加的电流是20mA,第二部分“S 2.0”是指电解液中NaCl浓度为2.0%,第三部分“H 3”是指电解液中添加的催化剂HNO 3浓度是3.0g/L。第四部分“T 40”是指实验过程中电解液的温度保持在40℃。详细的实验分组和实验参数见表8.1。 Similar to other chemical reactions, the chemical reaction process for the recovery of carbon fibers by electrochemical methods should also have suitable reaction conditions. The present invention determines the appropriate temperature for the electrochemical recovery process of the present invention by the following experimental results. Similarly, multiple sets of samples (shown in Table 6.1 below) were used to test the appropriate reaction temperatures, with current intensities of 20 mA and 40 mA, NaCl concentration of 2.0 (%), and HNO 3 dose of 3.0 g/L. The temperature gradient is a total of 6 sets of four temperature gradients that exclude extreme temperatures of extremely low yields (very low, such as below 0 ° C, and temperatures above 100 ° C). The sample number is determined by the action current, NaCl concentration, catalyst HNO 3 concentration and temperature gradient, such as the sample number “I20S 2.0 H 3 T 40 ”. The first part “I20” means the current applied by the sample is 20 mA, the second part “S 2.0 "refers to the electrolyte concentration of 2.0% NaCl, part III" H 3 "means that the catalyst is added to the electrolyte concentration of HNO 3 is 3.0g / L. The fourth part "T 40 " means that the temperature of the electrolyte is maintained at 40 ° C during the experiment. Detailed experimental groupings and experimental parameters are shown in Table 8.1.
表8.1实验样本分组及参数Table 8.1 Experimental sample grouping and parameters
Figure PCTCN2018075922-appb-000014
Figure PCTCN2018075922-appb-000014
本部分实验电化学回收周期为4天,回收结束后,复合材料进行硬度测试。然后去除复合材料的水泥基胶体,取出碳纤维。得到的回收得到的碳纤维清洗烘干,再进行各种测 试。经检测,回收得到的碳纤维仍然保持丝束状,长度大概为100mm,基本与样本回收长度一致,表面富有光泽,说明碳纤维在回收过程受到的氧化与腐蚀等损害很小。The electrochemical recovery period of this part was 4 days. After the recovery, the composite was tested for hardness. The cement-based colloid of the composite is then removed and the carbon fibers are removed. The recovered carbon fiber obtained is washed and dried, and various tests are performed. After testing, the recovered carbon fiber still maintains a tow shape with a length of about 100 mm, which is basically the same as the sample recovery length, and the surface is lustrous, indicating that the carbon fiber is less damaged by oxidation and corrosion during the recovery process.
8.1碳纤维增强水泥基复合材料样本及碳纤维回收量8.1 Carbon fiber reinforced cement-based composite samples and carbon fiber recovery
从表8.2可以看到,碳纤维增强水泥基复合材料样本在4天的回收周期后,硬度下降非常大,都远远小于9B硬度等级,I20S 2.0H 3T 75样本的内聚破坏深度达到1.88mm,接近碳纤维层,说明温度在碳纤维增强水泥基复合材料软化中起到巨大的影响,弥补了回收周期短的影响。同时从复合材料内聚破坏深度能够发现,温度越大,复合材料的软化程度越严重。 It can be seen from Table 8.2 that after 4 days of recovery cycle, the carbon fiber reinforced cement-based composite samples have a very large hardness drop, which is far less than the 9B hardness grade. The cohesive failure depth of the I20S 2.0 H 3 T 75 sample reaches 1.88 mm. Close to the carbon fiber layer, indicating that the temperature has a great influence on the softening of the carbon fiber reinforced cement-based composite material, and compensates for the short recovery cycle. At the same time, it can be found from the depth of cohesive failure of the composite material that the higher the temperature, the more severe the softening degree of the composite material.
表8.2复合材料样本硬度及内聚破坏深度Table 8.2 Composite material hardness and cohesive failure depth
Figure PCTCN2018075922-appb-000015
Figure PCTCN2018075922-appb-000015
注:铅笔硬度计的软硬度从低到高依次为:9B~8B~7B~6B~5B~4B~3B~2B~1B~HB~F~H~2H~3H~4H~5H~6H~7H~8H~9HNote: The hardness of the pencil hardness tester from low to high is: 9B to 8B to 7B to 6B to 5B to 4B to 3B to 2B to 1B to HB to F to H to 2H to 3H to 4H to 5H to 6H to 7H~8H~9H
从表8.3和图12看到,碳纤维回收量随温度的升高呈现先高后低趋势,在温度为T 40(40℃)时,碳纤维回收量最大,I20S 2.0H 3T 40回收量为772mg,达到碳纤维原丝的91.8%。高温状态下回收周期虽然只有常温(T 0,25℃)的一半,但是碳纤维的回收量更高,原因应该是碳纤维受到的电化学氧化作用时间越短,劣化程度越低,产生的毛丝越少,因而回收得到的量越多。I20系列样本的碳纤维回收量明显比I40系列高,尤其是在高温阶段,在碳纤维取出及清洗过程发现,I40系列碳纤维的毛丝较多,不但较多粘在水泥基凝胶上,并且一部分随水流冲走,表明大电流对碳纤维造成的劣化更严重。 As seen from Table 8.3 and Figure 12, the recovery of carbon fiber showed a high first and then low trend with increasing temperature. At the temperature of T 40 (40 ° C), the carbon fiber recovery was the largest, and the recovery of I20S 2.0 H 3 T 40 was 772 mg. , reaching 91.8% of the carbon fiber precursor. Although the recovery cycle at high temperature is only half of the normal temperature (T 0 , 25 ° C), the recovery of carbon fiber is higher. The reason is that the shorter the electrochemical oxidation time of the carbon fiber, the lower the degree of deterioration, and the more the resulting filament Less, so the amount recovered is more. The carbon fiber recovery of I20 series samples is obviously higher than that of I40 series, especially in the high temperature stage. In the process of carbon fiber extraction and cleaning, I40 series carbon fiber has more filaments, not only more cemented on cement-based gel, but also a part of The water flow washed away, indicating that the deterioration of the carbon fiber caused by the large current is more serious.
表8.3不同温度梯度条件下的碳纤维相关性能Table 8.3 Carbon fiber related properties under different temperature gradient conditions
Figure PCTCN2018075922-appb-000016
Figure PCTCN2018075922-appb-000016
注:1)DB:表示破坏模式为无机脂层剥离破坏Note: 1) DB: indicates that the failure mode is the peeling of the inorganic fat layer.
2)CB:表示破坏模式为碳纤维与无机脂界面剥离破坏2) CB: indicates that the failure mode is the interface peeling damage between carbon fiber and inorganic grease
8.2样本电压检测8.2 Sample voltage detection
从图13看到,各组样本电压较低,不同参数条件的样本电压差异值很小,表明在高温条件下,样本的系统阻值非常小。所有样本的电压在电化学回收周期基本保持稳定,I20系列样本电压波动在0.15V以内,I40系列样本电压波动在0.1V以内。相同温度条件的样本电压相接近,T 2系列样本的电压最低,表明在此条件下其导电性能非常好,碳纤维的劣化程度很低。 It can be seen from Fig. 13 that the sample voltage of each group is low, and the sample voltage difference value of different parameter conditions is small, indicating that the system resistance of the sample is very small under high temperature conditions. The voltage of all samples remained stable during the electrochemical recovery cycle. The I20 series sample voltage fluctuated within 0.15V, and the I40 series sample voltage fluctuated within 0.1V. The sample voltages of the same temperature conditions are close, and the voltage of the T 2 series samples is the lowest, indicating that the conductivity is very good under these conditions, and the degree of deterioration of carbon fibers is very low.
8.3回收得到的碳纤维单丝拉伸强度检测8.3 Recovered carbon fiber monofilament tensile strength test
从表8.4发现,碳纤维直径保持7μm不变,表明在电化学回收过程碳纤维受到的电化学氧化及酸的腐蚀等作用程度较轻,碳纤维表面基本没有片层剥落。回收得到的碳纤维中,I20S 2.0H 3T 3的单丝拉伸强度最高为3214MPa,达到碳纤维原丝的89.58%;I40S 2.0H 3T 1的拉伸强度最低为2881MPa,为碳纤维原丝的80.30%。其他回收得到的碳纤维的单丝拉伸强度相比碳纤维原丝均要低,较为直观的单丝拉伸强度与温度梯度的关系见图14。 It is found from Table 8.4 that the carbon fiber diameter remains unchanged at 7 μm, indicating that the electrochemical oxidation and acid corrosion of the carbon fiber during the electrochemical recovery process are less severe, and there is substantially no peeling of the surface of the carbon fiber. Among the recovered carbon fibers, the tensile strength of I20S 2.0 H 3 T 3 is up to 3,214 MPa, which is 89.58% of the carbon fiber precursor; the tensile strength of I40S 2.0 H 3 T 1 is 2,881 MPa, which is 80.30 of the carbon fiber precursor. %. The tensile strength of the monofilament of other recycled carbon fibers is lower than that of the carbon fiber precursor. The relationship between the tensile strength of the monofilament and the temperature gradient is shown in Fig. 14.
表8.4不同温度梯度条件下的回收碳纤维拉伸强度(ISO11566)Table 8.4 Tensile strength of recycled carbon fiber under different temperature gradient conditions (ISO11566)
Figure PCTCN2018075922-appb-000017
Figure PCTCN2018075922-appb-000017
从图14中可以明显看到,回收得到的碳纤维的单丝拉伸强度随温度的增加呈现先下降然后一直缓慢上升的趋势。需要指出,在常温T 0(25℃)条件下,碳纤维的回收周期为8天,高温条件下,回收周期缩短为4天,碳纤维受到的氧化和腐蚀等作用要弱一些,因此损伤相对较小,碳纤维的拉伸强度自然要高一些。然而,在温度为T 1(40℃)时,碳纤维的拉伸强度却比T 0时低,应该是在此温度下碳纤维受到了某种类型更为严重的劣化损伤。I20系列样本拉伸强度比I40系列高,而且随着温度升高,二者差值不断加大,可能是在高温条件下,大电流使样本的氧化反应速率加快。 As is apparent from Fig. 14, the tensile strength of the monofilament of the recovered carbon fiber showed a tendency to decrease first and then to rise slowly with an increase in temperature. It should be pointed out that under normal temperature T 0 (25 ° C), the recovery period of carbon fiber is 8 days. Under high temperature conditions, the recovery period is shortened to 4 days, and the carbon fiber is weakened by oxidation and corrosion, so the damage is relatively small. The tensile strength of carbon fiber is naturally higher. However, at a temperature of T 1 (40 ° C), the tensile strength of the carbon fiber is lower than that at T 0 , and the carbon fiber should be subjected to some type of more serious deterioration damage at this temperature. The tensile strength of the I20 series sample is higher than that of the I40 series, and as the temperature increases, the difference between the two increases continuously. It may be that under high temperature conditions, the large current makes the oxidation reaction rate of the sample faster.
8.4回收得到的碳纤维界面剪切性能分析8.4 Analysis of Interfacial Shear Properties of Carbon Fibers Recovered
从表8.5可以看到,回收得到的碳纤维中除了I40S 2.0H 3T 2的破坏模式为CB,其他样本的破坏模式均为DB。I20S 2.0H 3T 2的界面剪切强度最高为28.45MPa,是碳纤维原丝的105.02%,其他样本的界面剪切强度相比碳纤维原丝均出现不同程度的下降。 It can be seen from Table 8.5 that the destruction mode of the recovered carbon fiber except for I40S 2.0 H 3 T 2 is CB, and the failure modes of other samples are all DB. The interfacial shear strength of I20S 2.0 H 3 T 2 is up to 28.45 MPa, which is 105.02% of the carbon fiber precursor. The interfacial shear strength of other samples is different compared with the carbon fiber precursor.
表8.5不同温度梯度条件下的回收碳纤维界面剪切强度Table 8.5 Interfacial shear strength of recycled carbon fiber under different temperature gradient conditions
Figure PCTCN2018075922-appb-000018
Figure PCTCN2018075922-appb-000018
注:1)DB:表示破坏模式为环氧树脂层剥离破坏Note: 1) DB: indicates that the failure mode is the epoxy layer peeling damage
2)CB:表示破坏模式为碳纤维与环氧树脂界面剥离破坏2) CB: indicates that the failure mode is the peeling failure of the interface between carbon fiber and epoxy resin
从图15发现,回收得到的碳纤维的界面剪切强度随温度升高,出现先下降然后增高再下降趋势,高温样本高剪切强度比常温T 0样本,原因可能与高温样本的回收周期仅为常温样本一半,被氧化刻蚀的表面精细结构程度较低,粗糙度较低有关。从图16A和图16B可以看到,I20S 2.0H 3T 1和I40S 2.0H 3T 1的破坏界面为光滑的无机脂层,剪切强度较低,分别为22.78MPa和23.51MPa,为碳纤维原丝的84.09%和86.78%。从图16C和图16D看到,I20S 2.0H 3T 2和I40S 2.0H 3T 2的破坏模式分别为DB和CB,破坏界面粘结有很多针状的细长无机脂,这些针状树脂能够增大了破坏的表面积,起到类似钢筋月牙肋的作用,极大提高机械咬合力,所以样本的剪切强度得到提高,分别达到碳纤维原丝的105.02%和98.74%。在图16E和图16F中,I20S 2.0H 3T 3和I40S 2.0H 3T 3的破坏模式均为DB,无机脂层发生破坏,在破坏界面可以观察到少量的针状无机脂,界面剪切强度较高,分别为碳纤维原丝的92.69%和89.66%。 It is found from Fig. 15 that the interfacial shear strength of the recovered carbon fiber increases first and then increases and then decreases with the increase of temperature. The high shear strength of the high temperature sample is higher than that of the normal temperature T 0 sample. The reason may be that the recovery period of the high temperature sample is only Half of the sample at room temperature is related to the low degree of fine structure of the surface which is oxidized and etched, and the roughness is low. It can be seen from Fig. 16A and Fig. 16B that the fracture interface of I20S 2.0 H 3 T 1 and I40S 2.0 H 3 T 1 is a smooth inorganic lipid layer with low shear strength of 22.78 MPa and 23.51 MPa, respectively. 84.09% and 86.78% of the silk. As seen from Fig. 16C and Fig. 16D, the failure modes of I20S 2.0 H 3 T 2 and I40S 2.0 H 3 T 2 are DB and CB, respectively, and the rupture interface is bonded with a lot of acicular elongated inorganic grease, and these acicular resins can The damaged surface area is increased, which acts like a steel crescent rib, which greatly improves the mechanical bite force, so the shear strength of the sample is improved, reaching 105.02% and 98.74% of the carbon fiber precursor, respectively. In Fig. 16E and Fig. 16F, the failure modes of I20S 2.0 H 3 T 3 and I40S 2.0 H 3 T 3 are both DB, the inorganic lipid layer is destroyed, and a small amount of acicular inorganic lipid can be observed at the destruction interface. The strength is higher, which is 92.69% and 89.66% of the carbon fiber precursor, respectively.
8.5 SEM扫描检测8.5 SEM scan detection
从图17可以看到,回收得到的碳纤维非常干净,表面没有附着水泥凝胶颗粒,碳纤维表面没有发现裂纹裂缝和凹坑等缺陷,相比相同参数样本在常温T 0条件下表面有裂纹裂缝,表明回收得到的碳纤维受到的氧化和酸腐蚀等作用程度比较轻微,缩短回收周期能有效减少碳纤维受到的劣化,因此高温条件下的回收得到的碳纤维拉伸强度更高。 It can be seen from Fig. 17 that the recovered carbon fiber is very clean, the surface of the carbon fiber is not attached with cement gel particles, and no crack cracks and pits are found on the surface of the carbon fiber. Compared with the same parameter sample, there is a crack crack on the surface under normal temperature T 0 condition. It indicates that the recovered carbon fiber is slightly less affected by oxidation and acid corrosion, and shortening the recovery cycle can effectively reduce the deterioration of the carbon fiber, so that the carbon fiber recovered under high temperature conditions has higher tensile strength.
8.6 AFM扫描检测8.6 AFM scan detection
表8.6回收得到的碳纤维的粗糙度Table 8.6 Roughness of recovered carbon fiber
Figure PCTCN2018075922-appb-000019
Figure PCTCN2018075922-appb-000019
Figure PCTCN2018075922-appb-000020
Figure PCTCN2018075922-appb-000020
回收得到的碳纤维的AFM测试结果分别见表8.6和图18。在T 1回收得到的碳纤维系列图18A至图18D,回收过程的氧化刻蚀程度较轻,碳纤维表面的纵向沟槽结构较浅,凸起结构尺寸大概在20μm~50μm之间,I20S 2.0H 3T 1和I40S 2.0H 3T 1计算得到的粗糙度分别为134nm和149nm,与碳纤维原丝的粗糙度144nm相差不大,因此回收得到的碳纤维的界面剪切强度不高。当温度继续升高,图18E至图18H,I40碳纤维系列表面出现更深的纵向沟槽结构,宽度更大,I40S 2.0H 3T 2表面密布凸起结构,这些凸起结构的尺寸大概在100nm~300nm之间,I20S 2.0H 3T 2和I40S 2.0H 3T 2粗糙度分别为168nm和169nm,纵向沟槽和凸起结构提高了碳纤维机械咬合力,增大比表面积改善浸润性,因此在T 2系列碳纤维的剪切破坏界面能够粘结着针状的树脂,极大提高了碳纤维的界面剪切强度。当温度上升到T 3时,从图18I至图18L看到,碳纤维表面出现较大尺寸的膨胀凸起,还有不连续的沟槽结构,I20S 2.0H 3T 3和I40S 2.0H 3T 3粗糙度分别为184nm和192nm,这些结构增大了比表面积,加大浸润吸附树脂的范德华力,然而粗糙度过大会减小碳纤维与树脂的粘结能力,并且该类结构不利于机械咬合作用,界面剪切强度不太高。 The AFM test results of the recovered carbon fibers are shown in Table 8.6 and Figure 18, respectively. FIG carbon fiber series T 1 is recovered 18A to 18D, the etching degree of oxidation less recovery process, the longitudinal grooves of the surface structure of the carbon fiber shallow, raised structures size between about 20μm ~ 50μm, I20S 2.0 H 3 The roughness calculated by T 1 and I40S 2.0 H 3 T 1 is 134 nm and 149 nm, respectively, which is not much different from the roughness of 144 nm of the carbon fiber precursor. Therefore, the interfacial shear strength of the recovered carbon fiber is not high. When the temperature continues to rise, Figure 18E to Figure 18H, the surface of the I40 carbon fiber series has a deeper longitudinal groove structure with a larger width. The surface of the I40S 2.0 H 3 T 2 is densely convex. The size of these raised structures is about 100 nm~ between 300nm, I20S 2.0 H 3 T 2 and I40S 2.0 H 3 T 2 roughness 168nm and 169nm, respectively, longitudinal grooves and projections carbon fiber structure to improve the mechanical bite force, the specific surface area to improve wettability, and therefore T The shear failure interface of the 2 series carbon fiber can bond the needle-like resin, which greatly improves the interfacial shear strength of the carbon fiber. When the temperature rises to T 3 , as seen from Fig. 18I to Fig. 18L, large-sized expanded protrusions appear on the surface of the carbon fiber, and discontinuous groove structures, I20S 2.0 H 3 T 3 and I40S 2.0 H 3 T 3 The roughness is 184 nm and 192 nm, respectively. These structures increase the specific surface area and increase the van der Waals force of the infiltrated adsorption resin. However, the roughness excessively reduces the bonding ability of the carbon fiber to the resin, and the structure is disadvantageous for mechanical biting. The interface shear strength is not too high.
8.7 XPS扫描检测8.7 XPS scan detection
经检测,回收得到的碳纤维的扫描全谱及C1s高分辨窄谱见图19A至图19F,左列是样本的扫描全谱,右列则是其对应的C1s高分辨窄谱及其分峰拟合图。从扫描全谱图可以看到,图中主要有六种峰,即两个主峰:C(284.6eV)和O(532.0eV);四个次要峰:Si(99.5eV)、Cl(199.8eV)、Ca(347eV)和N(399.5eV)。碳纤维原丝的表面基本元素为碳和氧,检测出来的少量硅、氯、钙和钙是在实验过程中的引入。不同温度梯度的回收得到的碳纤维表面化学元素含量情况见表8.7。After scanning, the scanned full spectrum of the recovered carbon fiber and the high resolution narrow spectrum of C1s are shown in Fig. 19A to Fig. 19F. The left column is the full spectrum of the sample, and the right column is the corresponding high resolution narrow spectrum of C1s and its peak resolution. Figure. It can be seen from the scanning full spectrum that there are six main peaks in the figure, namely two main peaks: C (284.6 eV) and O (532.0 eV); four secondary peaks: Si (99.5 eV), Cl (199.8 eV). ), Ca (347 eV) and N (399.5 eV). The basic elements of the carbon fiber precursor are carbon and oxygen, and the small amount of silicon, chlorine, calcium and calcium detected is introduced during the experiment. See Table 8.7 for the chemical element content of the carbon fiber obtained by the recovery of different temperature gradients.
表8.7回收得到的碳纤维表面元素含量(%)Table 8.7 Surface Element Content of Carbon Fiber Recovered (%)
Figure PCTCN2018075922-appb-000021
Figure PCTCN2018075922-appb-000021
Figure PCTCN2018075922-appb-000022
Figure PCTCN2018075922-appb-000022
从表中可以看到,回收得到的碳纤维相比碳纤维原丝,C元素含量都有一定程度的下降,而氧元素含量出现较大幅度上升,从氧碳比来看,碳纤维原丝仅为0.2610,而氧碳比最低的I20S 2.0H 3T 3亦达到0.4066,为碳纤维原丝的1.5倍以上,说明回收得到的碳纤维表面引入了较多的氧,获得了更大活性。三个温度梯度样本中,I20S 2.0H 3T 2的氧碳比最高为0.4281,I20S 2.0H 3T 1稍低一些,氧碳比为0.4252,I20S 2.0H 3T 3则最低,从上面的实验知道I20S 2.0H 3T 0的氧碳比为0.3859,表明虽然回收周期缩短导致碳纤维氧化时间变短,但是高温条件反而使碳纤维表面的氧引入量更大,在温度为T 2时,碳纤维表面氧碳比最大,随后开始下降。在回收过程,碳纤维表面均引入了氯元素,氯含量随温度升高而下降。此外,I20S 2.0H 3T 2和I20S 2.0H 3T 3碳纤维表面还引入了少量氮、硅和钙元素。 It can be seen from the table that the recycled carbon fiber has a certain decrease in the content of C element compared with the carbon fiber precursor, and the oxygen content increases significantly. From the oxygen to carbon ratio, the carbon fiber precursor is only 0.2610. The lowest oxygen-to-carbon ratio of I20S 2.0 H 3 T 3 also reached 0.4066, which is more than 1.5 times that of the carbon fiber precursor. This indicates that more carbon is introduced into the surface of the recovered carbon fiber, and more activity is obtained. Among the three temperature gradient samples, the oxygen-to-carbon ratio of I20S 2.0 H 3 T 2 is 0.4281, I20S 2.0 H 3 T 1 is slightly lower, the oxygen-carbon ratio is 0.4252, and I20S 2.0 H 3 T 3 is the lowest. From the above experiment It is known that the oxygen-carbon ratio of I20S 2.0 H 3 T 0 is 0.3859, which indicates that although the recovery period shortens and the oxidation time of carbon fiber becomes shorter, the high-temperature condition causes the oxygen introduction amount on the surface of carbon fiber to be larger. At the temperature of T 2 , the surface oxygen of carbon fiber The carbon ratio is the largest and then begins to decline. During the recovery process, chlorine is introduced into the surface of the carbon fiber, and the chlorine content decreases as the temperature increases. Further, I20S 2.0 H 3 T 2 and I20S 2.0 H 3 T 3 surface of carbon fibers also introduces a small amount of nitrogen, silicon, and calcium.
根据文献以及已经进行的研究分析,利用软件XPSPeak4.1,将C1s高分辨窄谱依据结合能分为以下六种化学键峰进行高斯洛伦茨拟合:石墨态C~C(284.4eV)、非晶态C~C(284.8eV)、C=O(285.5eV)、C~O(286.2eV)、C~Cl(287.2)和O~C=O(288.4eV)。C1s分峰拟合见图6.9右列,具体的回收得到的碳纤维表面官能团含量见表8.8。According to the literature and the research that has been carried out, using the software XPSPeak4.1, the high resolution narrow spectrum of C1s is divided into the following six chemical bond peaks according to the binding energy: Gauss Lorenz fitting: Graphite state C~C (284.4eV), non Crystalline C to C (284.8 eV), C=O (285.5 eV), C to O (286.2 eV), C to Cl (287.2), and O to C=O (288.4 eV). The C1s peak fitting is shown in the right column of Figure 6.9. The specific recovered carbon fiber surface functional group content is shown in Table 8.8.
表8.8回收得到的碳纤维表面官能团含量(%)Table 8.8 Recovered carbon fiber surface functional group content (%)
Figure PCTCN2018075922-appb-000023
Figure PCTCN2018075922-appb-000023
从表中看到,相比碳纤维原丝表面的石墨态和非晶态C~C键总量为51.1%,I20S 2.0H 3T 1和I20S 2.0H 3T 2出现下降,均为44.9%,而I20S 2.0H 3T 3则稍微上升为51.4%;由于回收过程的电化学氧化,回收得到的碳纤维的C~O键均出现大幅度下降;而在C=O键中,I20S 2.0H 3T 1含量下降,I20S 2.0H 3T 2和I20S 2.0H 3T 3含量则略有上升;在强亲水性基团O~C=O键中,温度越低的回收得到的碳纤维含量越高,这是可能是因为在高温下O~C=O键更容易生成二氧化碳和水 [34],上述表明回收得到的碳纤维反应温度越低,其表面氧化程度越高,与无机脂的化学结合能力越强,然而由于I20S 2.0H 3T 1表面的C~Cl键含量高达8.2%,说明碳纤维受到了较为严重的氯化,造成拉伸强度和界面剪切强度下降,与之对应的I20S 2.0H 3T 2和I20S 2.0H 3T 3表面的氯并非以化学键结合,而是以吸附状态存在。 It can be seen from the table that the total amount of graphite and amorphous C-C bonds on the surface of the carbon fiber precursor is 51.1%, and the decrease of I20S 2.0 H 3 T 1 and I20S 2.0 H 3 T 2 is 44.9%. The I20S 2.0 H 3 T 3 increased slightly to 51.4%. Due to the electrochemical oxidation of the recovery process, the C~O bond of the recovered carbon fiber decreased greatly. In the C=O bond, I20S 2.0 H 3 T 1 content decreased, I20S 2.0 H 3 T 2 and I20S 2.0 H 3 T 3 content increased slightly; in the strong hydrophilic group O ~ C = O bond, the lower the temperature, the higher the recovered carbon fiber content, This is probably because the O~C=O bond is more likely to generate carbon dioxide and water at high temperatures [34] . The above indicates that the lower the reaction temperature of the recovered carbon fiber, the higher the surface oxidation degree, and the more chemical bonding ability with inorganic grease. Strong, however, because the C~Cl bond content on the surface of I20S 2.0 H 3 T 1 is as high as 8.2%, it indicates that the carbon fiber is subjected to more serious chlorination, resulting in a decrease in tensile strength and interfacial shear strength, and the corresponding I20S 2.0 H 3 chloro and T 2 I20S 2.0 H 3 T 3 is not chemically bonded to the surface, adsorbed form but in It exists.
8.8 XRD分析8.8 XRD analysis
从图20A和图20B可以看到,回收碳纤维的XRD光谱只有一个强衍射峰,峰位在 2θ=26°附近,经过物相检索,判定为C,表明在电化学回收过程,碳纤维表面并没有引入其他晶体结构化合物。It can be seen from Fig. 20A and Fig. 20B that the XRD spectrum of the recovered carbon fiber has only one strong diffraction peak, and the peak position is near 2θ=26°. After the phase retrieval, it is judged as C, indicating that the surface of the carbon fiber is not in the electrochemical recovery process. Other crystal structure compounds are introduced.
进一步地,从图中可知,回收碳纤维的结晶度都比较差。H 1系列回收碳纤维的衍射峰强度较低,当硝酸浓度增大到3g/L时,衍射峰强度增大,峰变得更尖一些,当硝酸浓度继续增大到5g/L时,衍射峰的强度下降,峰端部变得圆滑,表明H 3系列的碳纤维结晶度相对较好,过高或过低的硝酸浓度使碳纤维的石墨块状结构在回收过程受到的影响较大。 Further, as is clear from the figure, the crystallinity of the recovered carbon fibers is relatively poor. The diffraction peak intensity of H 1 series recycled carbon fiber is low. When the concentration of nitric acid increases to 3g/L, the intensity of the diffraction peak increases, and the peak becomes sharper. When the concentration of nitric acid continues to increase to 5g/L, the diffraction peak The strength of the peak decreases, and the peak end becomes smooth, indicating that the crystallinity of the carbon fiber of the H 3 series is relatively good, and the concentration of nitric acid which is too high or too low causes the graphite block structure of the carbon fiber to be greatly affected in the recovery process.
值得一提的是,在上述继续通电进行回收的实验中,所使用的电解装置可为本领域所熟知的各种电解池、电解槽等。It is worth mentioning that in the above experiments in which the power is continuously recovered, the electrolyzer used may be various electrolytic cells, electrolytic cells, and the like which are well known in the art.
作为回收容器的上述电解装置中装有预先设计的回收剂和催化剂相混合的化学溶液,其可以有效侵入待回收的所述碳纤维增强水泥基复合材料的水泥基胶凝材料,并破坏其化学键,促使水泥基胶凝材料分解。所述化学溶液包括但不局限于水、HNO 3(硝酸)、液体乙醇、液体乙二醇、各种酸性溶液(包括但不局限于H 2Si 3(偏硅酸)、HCN(氢氰酸)、H 2C 3(碳酸)、HF(氢氟酸)、C 3COOH(也作C 2H 4O 2乙酸,又叫醋酸)、H 2S(氢硫酸)、HClO(次氯酸)、HNO 2(亚硝酸)、所有的有机酸、H 2S 3(亚硫酸)等)、各种碱性溶液(包括但不局限于氢氧化钾溶液、氢氧化钠溶液等)、各种含氯离子溶液(包括但不局限于氯化钠溶液、氯化锌溶液等)。上述化学液体的特征为可以是上述各种溶液的混合溶液,各种溶液的浓度为0.001%-99.9%, The above electrolysis device as a recovery container is provided with a chemical solution in which a pre-designed recyclant and a catalyst are mixed, which can effectively invade the cement-based cementing material of the carbon fiber reinforced cement-based composite material to be recovered, and destroy the chemical bond thereof. Promote the decomposition of cement-based cementitious materials. The chemical solution includes, but is not limited to, water, HNO 3 (nitric acid), liquid ethanol, liquid ethylene glycol, various acidic solutions (including but not limited to H 2 Si 3 (metasilicate), HCN (hydrocyanic acid). ), H 2 C 3 (carbonic acid), HF (hydrofluoric acid), C 3 COOH (also known as C 2 H 4 O 2 acetic acid, also known as acetic acid), H 2 S (hydrogen sulfuric acid), HClO (hypochlorous acid) , HNO 2 (nitrous acid), all organic acids, H 2 S 3 (sulfurous acid), etc., various alkaline solutions (including but not limited to potassium hydroxide solution, sodium hydroxide solution, etc.), various Chloride solution (including but not limited to sodium chloride solution, zinc chloride solution, etc.). The above chemical liquid is characterized by being a mixed solution of the above various solutions, and the concentration of each solution is 0.001% to 99.9%,
根据本发明的该优选实施例,在通电过程中,待回收的所述碳纤维增强水泥基复合材料中的碳纤维材料采用所熟知的方法与电源的正极连接,以确保在回收过程中电路稳定运行。所述纤维材料与电源的正极进行连接的方法包括但不局限于溶解树脂、磨去树脂等,以暴露出内部纤维材料,便于电路连接。According to this preferred embodiment of the invention, the carbon fiber material in the carbon fiber reinforced cementitious composite material to be recovered is connected to the positive electrode of the power source in a well-known manner during the energization process to ensure stable operation of the circuit during the recovery process. The method of joining the fiber material to the positive electrode of the power source includes, but is not limited to, dissolving the resin, grinding away the resin, etc., to expose the inner fiber material to facilitate circuit connection.
根据本发明的该优选实施例,通电过程中的阴极材料为熟知的导电材料,包括但不局限于钢材、铁、各种金属、各种形式石墨材料。In accordance with this preferred embodiment of the invention, the cathode material during energization is a well known conductive material including, but not limited to, steel, iron, various metals, various forms of graphite materials.
所述通电过程中,电流密度大小的特征在于与上述化学溶液的共同作用下,可以促使待回收的所述碳纤维增强水泥基复合材料中的水泥基胶凝材料解,同时不影响回收碳纤维的各种力学性能、导电性能、与有机(环氧树脂)和无机(水泥基)胶凝材料的粘接性能和再加工性能。所述电流密度的大小根据所述碳纤维增强无机(水泥基)复合材料中碳纤维材料浸泡于所述电解液内的表面积大小进行计算,范围为3333.3~6666.7mA/m 2During the electrification process, the current density is characterized by cooperating with the chemical solution to promote the solution of the cement-based cementitious material in the carbon fiber reinforced cement-based composite material to be recovered, without affecting each of the recovered carbon fibers. Mechanical properties, electrical conductivity, adhesion to organic (epoxy) and inorganic (cement based) cementitious materials and reworkability. The magnitude of the current density is calculated according to the surface area of the carbon fiber reinforced inorganic (cement-based) composite material in which the carbon fiber material is immersed in the electrolyte, and ranges from 3333.3 to 6666.7 mA/m 2 .
所述通电过程中,通电时间的特征是在与上述化学溶液和电流的共同作用下,可以促使待回收的所述碳纤维增强水泥基复合材料中的水泥基胶凝材料分解,同时不影响回收碳 纤维的各种力学性能、导电性能、与有机(环氧树脂)和无机(水泥基)胶凝材料的粘接性能和再加工性能。所述通电时间为0.5~200小时,优选为2-120小时,更优选为4–48小时。During the electrification process, the energization time is characterized in that, in combination with the above chemical solution and current, the cement-based cementitious material in the carbon fiber reinforced cement-based composite material to be recovered can be decomposed without affecting the recycled carbon fiber. Various mechanical properties, electrical conductivity, adhesion to organic (epoxy) and inorganic (cement based) cementitious materials and reworkability. The energization time is from 0.5 to 200 hours, preferably from 2 to 120 hours, more preferably from 4 to 48 hours.
所述通电过程中,可采用各种本行业熟知的树脂老化方法加快回收速度,例如紫外线强化、超声强化、微波强化。During the energization process, various resin aging methods well known in the art can be used to speed up the recovery, such as ultraviolet ray strengthening, ultrasonic strengthening, and microwave strengthening.
在所述自碳纤维增强水泥基复合材料中回收碳纤维的方法中,反应温度为25℃~75℃,优选为40℃~75℃,更优选为60℃~75℃。In the method for recovering carbon fibers from the carbon fiber reinforced cement-based composite material, the reaction temperature is from 25 ° C to 75 ° C, preferably from 40 ° C to 75 ° C, more preferably from 60 ° C to 75 ° C.
所述回收容器中的压力调整至预设大小,其与上述化学溶液、电流和温度的共同作用下,促使待回收的所述碳纤维增强水泥基复合材料中的水泥基胶凝材料发生膨胀和分解,同时不影响回收碳纤维的各种力学性能、导电性能、与树脂材料的粘接性能和再加工性能。其压力范围为0.5~20大气压,加压时间为0.5~200小时。The pressure in the recovery container is adjusted to a preset size, which, together with the above chemical solution, current and temperature, causes expansion and decomposition of the cement-based cementitious material in the carbon fiber reinforced cement-based composite material to be recovered. At the same time, it does not affect the various mechanical properties, electrical conductivity, adhesion to resin materials and reworkability of recycled carbon fibers. The pressure ranges from 0.5 to 20 atm and the pressurization time is from 0.5 to 200 hours.
所述电化学回收方法中,阳极与阴极材料间距离对回收效果、回收速度和回收成本有影响,优选为1mm~1000mm,更优选为20mm~60mm。In the electrochemical recovery method, the distance between the anode and the cathode material has an effect on the recovery effect, the recovery rate, and the recovery cost, and is preferably from 1 mm to 1000 mm, and more preferably from 20 mm to 60 mm.
此外,所述电化学回收方法中,将碳纤维取出后保存,即可投入再生产。所述取出方法为各种所熟知的方法,包括且不局限于超声、干燥、加热等、以及各种方法的结合。Further, in the electrochemical recovery method, the carbon fiber is taken out and stored, and then it can be put into production. The method of removal is a variety of well known methods including, but not limited to, ultrasound, drying, heating, and the like, as well as combinations of various methods.
回收得到的碳纤维的长度是其再利用价值的一个重要因素。对回收得到的碳纤维,进行拉直,可以看到碳纤维的长度大约在80mm~100mm之间,而实验设计的样本回收部分长度为100mm,考虑到在剪取回收得到的碳纤维存在的长度损耗,可以知道在电化学回收过程碳纤维的长度基本没有损耗,表明在整个回收过程,碳纤维遭受的电化学氧化等损害非常轻微。The length of the recovered carbon fiber is an important factor in its reuse value. The carbon fiber recovered is straightened, and the length of the carbon fiber is about 80 mm to 100 mm. The length of the sample recovery part of the experimental design is 100 mm. Considering the length loss of the carbon fiber obtained by the shear recovery, It is known that there is substantially no loss in the length of the carbon fiber during the electrochemical recovery process, indicating that the damage caused by the electrochemical oxidation of the carbon fiber is very slight throughout the recovery process.
根据本发明的该优选实施例,在自碳纤维增强水泥基复合材料中回收碳纤维的方法中,所述电解液含有1g/L~5g/L的催化剂B,其中该催化剂B为可溶性酸,可以是但不限于是HNO 3。如说明书附图之图4和图6所示,不同分组碳纤维增强水泥基复合材料样本回收得到的碳纤维的量有所不同,碳纤维回收量随HNO 3浓度增大呈现先增后降趋势,HNO 3浓度为3g/L时,碳纤维回收量最大。在HNO 3浓度为1g/L分组中,碳纤维回收量明显降低,且回收得到的碳纤维的单丝拉伸强度随HNO 3浓度增大而呈下降趋势,在0~3(g/L)的HNO 3浓度区间,碳纤维的拉伸强度下降幅度较小,3~5(g/L)的HNO 3浓度区间,回收得到的碳纤维拉伸强度急剧下降。因此,HNO 3的浓度控制在1~3(g/L)时较优,更优选地被控制在3g/L时,可获得理想的回收效果。 According to the preferred embodiment of the present invention, in the method for recovering carbon fibers from a carbon fiber reinforced cement-based composite material, the electrolyte solution contains 1 g/L to 5 g/L of catalyst B, wherein the catalyst B is a soluble acid, which may be But not limited to HNO 3 . As shown in Figure 4 and Figure 6 of the drawings, the amount of carbon fiber recovered from different carbon fiber reinforced cement-based composite samples is different, and the amount of carbon fiber recovered increases first and then decreases with the increase of HNO 3 concentration. HNO 3 At a concentration of 3 g/L, the amount of carbon fiber recovered is the largest. In the HNO 3 concentration of 1g / L group, the carbon fiber recovery amount was significantly reduced, and the tensile strength of the recovered carbon fiber filaments decreased with the increase of HNO 3 concentration, and the HNO at 0-3 (g/L) In the concentration range of 3 , the tensile strength of carbon fiber decreased slightly, and the tensile strength of the recovered carbon fiber decreased sharply in the range of HNO 3 concentration of 3 to 5 (g/L). Therefore, the concentration of HNO 3 is preferably controlled at 1 to 3 (g/L), and more preferably controlled at 3 g/L, whereby an ideal recovery effect can be obtained.
本领域技术人员会明白附图中所示的和以上所描述的本发明实施例仅是对本发明的 示例而不是限制。Those skilled in the art will appreciate that the embodiments of the invention, which are illustrated in the figures and described above, are merely illustrative and not limiting.
由此可以看到本发明目的可被充分有效完成。用于解释本发明功能和结构原理的该实施例已被充分说明和描述,且本发明不受基于这些实施例原理基础上的改变的限制。因此,本发明包括涵盖在附属权利要求书要求范围和精神之内的所有修改。It can thus be seen that the object of the invention can be fully and efficiently accomplished. The embodiment has been described and described in detail to explain the principles of the present invention and the invention is not to be construed as limited. Accordingly, the present invention includes all modifications that come within the scope and spirit of the appended claims.

Claims (10)

  1. 一种自无机胶凝材料中回收高性能碳纤维的方法,其包括下述步骤:A method for recovering high performance carbon fibers from an inorganic cementitious material, comprising the steps of:
    (A)将碳纤维增强无机复合材料置于电解液中,其中该电解液含有重量比为0.5%~3%的NaCl和1.0g/L~5g/L的催化剂;;(A) placing a carbon fiber-reinforced inorganic composite material in an electrolyte, wherein the electrolyte contains 0.5% to 3% by weight of NaCl and 1.0 g/L to 5 g/L of the catalyst;
    (B)对放置在电解液中的碳纤维增强无机复合材料通电,其中该碳纤维增强无机复合材料与电源的正极相连,并控制电流密度为3333.3~6666.7mA/m 2;和 (B) energizing the carbon fiber reinforced inorganic composite material placed in the electrolyte, wherein the carbon fiber reinforced inorganic composite material is connected to the positive electrode of the power source, and the current density is controlled to be 3333.3 to 6666.7 mA/m 2 ;
    (C)通电反应0.5-200小时后,自该电解液中取出碳纤维回收物。(C) After the energization reaction was carried out for 0.5 to 200 hours, the carbon fiber recovered product was taken out from the electrolytic solution.
  2. 根据权利要求1所述的方法,其特征在于,进一步包括下述步骤:The method of claim 1 further comprising the step of:
    (D)在碳纤维回收物表面插孔后,水流冲洗,以除去水泥基无机胶,其中孔间距为大于0.1mm,水流水压高于0.1MPa,冲洗时间不少于3秒。(D) After the surface of the carbon fiber recyclate is filled, the water is washed to remove the cement-based inorganic rubber, wherein the pore spacing is greater than 0.1 mm, the water flow pressure is higher than 0.1 MPa, and the rinsing time is not less than 3 seconds.
  3. 根据权利要求1所述的方法,其特征在于,该电解液进一步含有1.0g/L~5g/L的催化剂,其中该催化剂系选自由氢氰酸、碳酸、氢氟酸、氢硫酸、次氯酸、亚硝酸、亚硝酸、偏硅酸和可溶性有机酸组成的群组。The method according to claim 1, wherein the electrolyte further comprises 1.0 g/L to 5 g/L of a catalyst, wherein the catalyst is selected from the group consisting of hydrocyanic acid, carbonic acid, hydrofluoric acid, hydrosulfuric acid, and hypochlorous. A group consisting of acid, nitrous acid, nitrous acid, metasilicate, and soluble organic acids.
  4. 根据权利要求2所述的方法,其特征在于,该电解液进一步含有1.0g/L~5g/L的催化剂,其中该催化剂系选自由氢氰酸、碳酸、氢氟酸、氢硫酸、次氯酸、亚硝酸、亚硝酸、偏硅酸和可溶性有机酸组成的群组。The method according to claim 2, wherein the electrolyte further contains 1.0 g/L to 5 g/L of the catalyst, wherein the catalyst is selected from the group consisting of hydrocyanic acid, carbonic acid, hydrofluoric acid, hydrosulfuric acid, and hypochlorous. A group consisting of acid, nitrous acid, nitrous acid, metasilicate, and soluble organic acids.
  5. 根据权利要求1至4中任一所述的方法,其特征在于,反应温度为25℃~75℃。The method according to any one of claims 1 to 4, wherein the reaction temperature is from 25 ° C to 75 ° C.
  6. 根据权利要求5所述的方法,其特征在于,反应温度为60℃~75℃。The method according to claim 5, wherein the reaction temperature is from 60 ° C to 75 ° C.
  7. 根据权利要求1所述的方法,其特征在于,该电解液含有重量比为0.5~3%的可溶性盐酸盐和1.0g/L~5g/L的催化剂,其中该催化剂系选自由氢氰酸、碳酸、氢氟酸、氢硫酸、次氯酸、亚硝酸、亚硝酸、偏硅酸和可溶性有机酸组成的群组,反应温度被控制为25℃~75℃。The method according to claim 1, wherein the electrolyte contains a soluble hydrochloride of 0.5 to 3% by weight and a catalyst of 1.0 g/L to 5 g/L, wherein the catalyst is selected from the group consisting of hydrocyanic acid. A group consisting of carbonic acid, hydrofluoric acid, hydrosulfuric acid, hypochlorous acid, nitrous acid, nitrous acid, metasilicate, and soluble organic acid, and the reaction temperature is controlled to be 25 ° C to 75 ° C.
  8. 根据权利要求1所述的方法,其特征在于,该电解液含有重量比为0.5%~3%的可溶性盐酸盐和1.0g/L~5g/L的催化剂,其中该催化剂系选自由氢氰酸、碳酸、氢氟酸、氢硫酸、次氯酸、亚硝酸、亚硝酸、偏硅酸和可溶性有机酸组成的群组,反应温度被控制为60℃~75℃。The method according to claim 1, wherein the electrolyte contains 0.5% to 3% by weight of soluble hydrochloride and 1.0%/L to 5 g/L of the catalyst, wherein the catalyst is selected from the group consisting of hydrocyanide. The reaction temperature is controlled to be 60 ° C to 75 ° C in the group consisting of acid, carbonic acid, hydrofluoric acid, hydrosulfuric acid, hypochlorous acid, nitrous acid, nitrous acid, metasilicate and soluble organic acid.
  9. 一种用于自无机胶凝材料中回收高性能碳纤维的电解液,其特征在于,其至少含有:An electrolyte for recovering high performance carbon fibers from an inorganic cementitious material, characterized in that it contains at least:
    重量比为0.5%~3%的可溶性盐酸盐;a soluble hydrochloride salt in a weight ratio of 0.5% to 3%;
    1.0g/L~5g/L的催化剂,其中该催化剂系选自由氢氰酸、碳酸、氢氟酸、氢硫酸、次氯酸、亚硝酸、亚硝酸、偏硅酸和可溶性有机酸组成的群组;和a catalyst of 1.0 g/L to 5 g/L, wherein the catalyst is selected from the group consisting of hydrocyanic acid, carbonic acid, hydrofluoric acid, hydrosulfuric acid, hypochlorous acid, nitrous acid, nitrous acid, metasilicate, and soluble organic acid. Group; and
    80%~98%的水。80% to 98% water.
  10. 根据权利要求9所述的电解液,其特征在于,优选含有3g/L的催化剂。The electrolytic solution according to claim 9, which preferably contains 3 g/L of a catalyst.
PCT/CN2018/075922 2018-02-09 2018-02-09 Method for recovering high-performance carbon fiber from inorganic cementing material WO2019153217A1 (en)

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